Human Health Risk Assessment Evaluation Of Potential Risks From Multipathway Exposure To Emissions Volume 5

United States                                                   EPA-905-R97-002e
Environmental Protection Agency                                     May 1997

WASTE MANAGEMENT
Risk Assessment for the Waste Technologies Industries (WTI)
Hazardous Waste Incineration Facility (East Liverpool, Ohio)
VOLUME V:
Human Health Risk Assessment: Evaluation of Potential Risks from
Multipathway Exposure to Emissions
                  U.S. Environmental Protection Agency - Region 5
                      Waste, Pesticides and Toxics Division
                            77 West Jackson Blvd.
                              Chicago, IL 60604
                           Prepared with the assistance of:

                     AT. Kearney, Inc. (Prime Contractor; Chicago, IL);
                           with Subcontract support from:
                           ENVIRON Corp. (Arlington, VA),
                      Midwest Research Institute (Kansas City, MO)
                        and EARTH TECH, Inc. (Concord, MA)
                         under EPA Contract No. 68-W4-0006

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VOLUME V
HUMAN HEALTH RISK ASSESSMENT:
EVALUATION OF POTENTIAL RISKS FROM MULTIPATHWAY
EXPOSURE TO EMISSIONS

CONTENTS
Page

I. INTRODUCTION M
A. Overview of Volume V 1-1

n. RISK ASSESSMENT METHODOLOGY H-l
A. The Risk Assessment Process H-l
B. Other U.S. EPA Guidance Documents H-2

m. TOXICTTY ASSESSMENT ffl-1
A. Toxicity Assessment Methods ffl-1
1. Carcinogenic Effects ffl-1
2. Noncarcinogenic Effects ffl-2
B. Toxicity Values for Substances of Potential Concern in Stack Emissions ffl-4
1. Dioxins and Furans ffl-4
2. Polycyclic Aromatic Hydrocarbons (PAHs) ffl-7
3. Lead ffl-8
4. Mercury ffl-9
5. Nickel ffl-9
6. Chromium ffl-9
7. Acid Gases ffl-10
8. Paniculate Matter ffl-10
C. Toxicity Assessment for Substances of Potential Concern in Fugitive
Emissions ffl-10
1. Fugitive Organic Chemical Emissions ffl-10
2. Fugitive Ash Emissions ffl-11
D. Uncertainties ffl-11
1. Uncertainties in the Characterization of the Toxicity
of Carcinogens ffl-12
2. Uncertainties in the Characterization of the Toxicity
of Noncarcinogens TTT-13
3. Uncertainties Associated with Route-to-Route Extrapolation ffl-14
4. Uncertainties Associated with Substances without'
Toxicity Values ffl-15
5. Uncertainties Associated with Endocrine Disrupters ffl-16
Volume V

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CONTENTS
(continued)
IV. SELECTION OF SURROGATE CHEMICALS IV-1
A. Selection of Chemicals in Stack Emissions to Evaluate in the
Risk Assessment IV-1
B. Partitioning of Emissions Between the Vapor and Particle Phases IV-5
C. Selection of Chemicals to Evaluate in Fugitive Emissions Analysis IV-5
1. Selection of Surrogate Chemicals in Fugitive Vapor Emissions IV-5
2. Estimation of Chemical-Specific Fugitive Organic Vapor
Emission Rates IV-8
3. Estimation of Chemical-Specific Emission Rates in Fugitive Ash IV-9
D. Uncertainties IV-10
1. Uncertainties Associated with the Selection of Surrogate Organic
Chemicals in Stack and Fugitive Emissions IV-10
2. Uncertainties Associated with Estimating Chemical-Specific
Fugitive Emission Rates IV-11

V. IDENTIFICATION OF EXPOSURE POPULATIONS AND PATHWAYS V-l
A. Introduction V-l
B. Population Subgroups Potentially Exposed to Stack Emissions V-l
C. Potential Exposure Routes for Stack Emissions V-3
1. Air Exposure Routes V-3
2. Soil Exposure Routes V-3
3. Terrestrial Food Chain Exposure Routes V-3
4. Surface Water Exposure Routes V-3
5. Breast Milk Exposure Route V-4
6. Fish Consumption Exposure Route V-4
7. Ground Water Exposure Route • V-5
D. Population Subgroups Potentially Exposed to Fugitive Emissions V-5
E. Uncertainties V-6
1. Uncertainties in the Identification of Exposure Populations V-6
2. Uncertainties in the Identification of Exposure Pathways V-6

VI. ESTIMATION OF ENVIRONMENTAL CONCENTRATIONS VI-1
A. Introduction VI-1
B. Estimation of Soil Concentrations VI-2
C. Estimation of Concentrations in Vegetation VI-3
D. Estimation of Meat, Eggs and Milk Concentrations '"" VI-7
E. Estimation of Surface Water Concentrations VI-9
F. Estimation of Chemical Concentrations in Fish VI-11
G. Estimation of Breast Milk Concentrations VI-12
Volume V

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CONTENTS
(continued)
H. Uncertainties VI -13
1. Uncertainties Inherent in the Fate and Transport Models VI-14
2. Uncertainties in Input Parameters VI-15

\TI. ESTIMATION OF EXPOSURE DOSE VIM
A. Introduction VH-\
B. Estimation of Human Exposure vn-2
1. Estimation of Exposure Dose vn-2
2. Exposure Factors V13-9
C. Site-Specific Exposure Data VH-10
1. Home Gardening Practices VH-10
2. Local Fishing Practices VH-11
3. Local Farming Practices VII-12
4. Deer Hunting VH-16
5. Population Data VII-16
D. Development of the Risk Assessment Study Area and Subareas VII-16
1. Development of the Risk Assessment Study Area VII-17
2. Development of Subareas VII-18
3. Development of Subareas for Assessment of Fugitive Emissions VII-19
E. Estimation of Exposure Doses in Subareas VH-19
1. Estimation of Contaminant Dispersion/Deposition in Subareas VII-19
2. Estimation of Exposure Dose VII-20
F. Uncertainties VEI-20

VIE. RISK CHARACTERIZATION VIH-l
A. Introduction VIH-1
B. Estimation of Risks Due to Stack Emissions Vin-2
1. Methodology for Estimating Individual Cancer Risk Vin-2
2. Methodology for Estimating Individual Noncancer Effects Vin-3
3. Methodology for Estimating Population Cancer Risk Vm-4
C. Overview of Individual Risks Associated with Stack Gas Emissions VTII-5
1. Risks Due to Direct (Inhalation) Exposure VTJ3-6
2. Risks Due to Indirect Exposure VHI-8
3. Sensitivity Analysis of Exposure Parameters for the Highly
Exposed Subgroups Vni-11
4. Estimation of the Potential Health Effects Due to Lead VHI-12
5. Risks Associated with Specific Activities VQI-14
D. Overview of Population Risks Vm-18
Volume V

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CONTENTS
(continued)
E. Estimation of Risks Due to Fugitive Emissions vm-20
1. Estimated Risks Due to Fugitive Organic Vapor Emissions VTQ-21
1. Risks Due to Fugitive Ash Emissions VHI-21
F. Uncertainties VTfl-23
1. Uncertainties Associated with the Risk Characterization Process VD3-23
2. Uncertainties Associated with the Risk Estimates VTII-27
3. Uncertainties Associated with the Uncharacterized Emissions Vffl-27
4. Uncertainties Associated with the Selection of Surrogate
Chemicals Vnt-28
5. Uncertainties Associated with Characterizing Breast Milk
Ingestion Risks vm-29
6. Uncertainties Associated with Methylmercury Risks VHI-30
G. Comparison of Incremental Dioxin and Furan Exposure to
Expected Background Exposure VHI-31

IX. UNCERTAINTY ANALYSIS IX-1
A. Introduction IX-1
1. Types and Sources of Uncertainty and Variability IX-1
2. Uncertainty and the Risk Assessment Process IX-2
B. A Three-Tiered Approach to Uncertainty Analysis IX-6
1. Tier I—Quantification of Input Parameter Variances IX-7
2. Tier 13—Sensitivity Analysis IX-7
3. Tier HI—Variance Propagation IX-9
C. Implementation of Tiered Approach to Uncertainty Analysis IX-10
D. Results IX-12
1. Estimation of Input Parameter Ranges IX-12
2. Sensitivity Analysis IX-12
3. Variance Propagation IX-15
E. Major Assumptions and Limitations IX-29
F. Conclusions IX-29

X. SUMMARY AND CONCLUSIONS X-l

XI. REFERENCES XI-1
Volume V

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                                    TABLES
Table 1-1         Substances of Potential Concern in Stack Emissions                   1-4
Table 1-2         Fugitive Substances of Potential Concern                             1-6
Table m-1       Summary of Inhalation and Oral Toxicity Values                   ffl-18
Table IH-2       Toxicity Equivalence Factors (TEFs) for Dioxins and Furans        HI-25
Table ffl-3       Relative Potency of Carcinogenic Polycyclic Aromatic
                 Hydrocarbons (PAHs)                                           ffl-26
Table ni-4       Summary of Inhalation Toxicity Values for Substances of.
                 Potential Concern (Fugitive Vapor Emissions)                      HI-27
Table ffl-5       Summary of Inhalation Toxicity Values for Metals  of Potential
                 Concern (Fugitive Ash Emissions)                                ffl-31
Table ffl-6       Key Assumptions for Chapter ffl (Toxicity Assessment)             ffl-32
Table IV-1       Selection of Surrogate Organic Chemicals (Stack Emissions) on
                 the Basis of Quantity, Carcinogenic Potency, and
                 Bioaccumulation Potential                                       IV-12
Table IV-2       Selection of Surrogate Organic Chemicals (Stack Emissions) on
                 the Basis of Quantity, Noncarcinogenic Potency, and
                 Bioaccumulation Potential                                       IV-13
Table IV-3       Surrogate Chemicals Selected for the Indirect Risk  Assessment
                 of Stack Emissions                                              IV-14
Table IV-4       Fraction of Substance Partitioning onto Paniculate Matter           IV-15
Table IV-5       Selection of Surrogate Chemicals (Fugitive Emissions) Based on
                 Quantity, Vapor Pressure, and  Carcinogenic Potency               IV-16
Table IV-6       Selection of Surrogate Chemicals (Fugitive Emissions) Based on
                 Quantity, Vapor Pressure, and  Noncancer Chronic  Toxicity
                 Potency                                                       IV-17
Table IV-7       Surrogate Chemicals Selected for the Assessment of Fugitive
                 Organic Vapor Emissions                                        IV-18
Table IV-8       Estimated Total Fugitive Organic Vapor Emissions  Rates            IV-19
Table IV-9       Estimated CAB Emissions Associated with the  Organic Waste
                 Tanks                                                         IV-20
Table IV-10      Estimated Fraction of Total Emissions  Due to Individual
                 Surrogate Chemicals                                            IV-21
Table IV-11      Estimated Emissions of Surrogate Chemicals from Fugitive
                 Organic Vapor Emissions Sources                             .   IV-22
Table IV-12      Detection Limits Used in Analysis of ESP Flyash Samples           IV-23
Table IV-13      Estimated Average Concentrations of Metals and Inorganic
                 Compounds in Fugitive Fly Ash Emissions                         IV-26
Table IV-14      Key Assumptions for Chapter IV (Selection of Surrogate
                 Chemicals)                                                     IV-27
Volume V

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                                    TABLES
                                     (continued)
 Table V-l        Exposure Populations and Pathways Considered in the Risk
                 Assessment                                                      V-8
 Table V-2        Key Assumptions for Chapter V (Identification of Exposure
                 Pathways and Populations)                                        V-9
 Table VI-1       Site-Specific Parameters for Fate and Transport Modeling          VI-17
 Table VI-2       Key Assumptions for Chapter VI (Estimation of Environmental
                 Concentrations)                                                VI-20
 Table VII-1       Typical Exposure Factors for which Site-Specific Data are
                 Available                                                     "VTI-22
 Table VTI-2       Results of East Liverpool Board of Health Vegetable Garden
                 Survey                                                       VII-23
 Table VH-3       Portion of Diet from Home Garden                              VTI-24
 Table VII-4       Summary of Ohio River Recreational Fishing Study Data          VTI-25
 Table VH-5       State-wide Beef Statistics                                       VH-26
 Table Vn-6       Estimated County Beef Statistics                                VII-27
 Table VTI-7       Summary of Beef Fanning Data, Beaver Valley Nuclear Power
                 Station Survey                                                VTJ-28
 Table VH-8       State-wide Milk Data                                          VH-31
 Table VTI-9       Estimated County Dairy Statistics                               VTI-32
 Table VII-10      Summary of Dairy Farming  Data, Beaver Valley Power Station
                 Survey                                                       VII-33
 Table VCI-11      Number of Dairy Farmers and Milk Production Range for Three
                 Counties Surrounding WTI Facility (May 1994)                  vn-34
 Table VH-12      Estimation of Meat from  Deer Hunted Locally                    VII-35
 Table VII-13      Summary of County  Population Data                            V13-36
 Table VII-14      Average and Maximum Air Dispersion/Deposition Impacts in
                 East Subareas                                                 VH-37
 Table VII-15      Average and Maximum Air Dispersion/Deposition Impacts in
                 North Subareas                                                VH-38
Table VII-16      Average and Maximum Air Dispersion/Deposition Impacts in
                 South Subareas                                                VQ-39
Table VII-17      Average and Maximum Air Dispersion/Deposition Impacts in
                 West Subareas                                                VH-40
Table VII-18      Chemical-specific Lifetime Average  Daily Dose (LADD) for
                 Carcinogens, Adult Subsistence Farmer in Subarea El
                 (Average Concentration)                        '               VI3-41
Table VII-19      Chemical-specific Average Daily Dose (ADD) for Noncarcinogens,
                 Adult  Subsistence Farmer at Subarea El (Average Concentration)   VJI-43
Table VH-20      Key Assumptions for Chapter VH (Estimation of Exposure Dose)   VH-45
Volume V

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                                    TABLES
                                     (continued)
 Table VTfl-1

 Table vm-2

 Table vm-3

 Table VTfl-4

 Table VHI-5

 Table VHI-6

 Table Vm-7

 Table VIH-g
 Table VHI-9

 Table VIE-10

 Table Vm-11

 Table VHI-12

 Table Vm-13

 Table VHI-14


 Table VHI-15
Table VHI-16
Table VHI-17
Table VH[-18
 Target Organ(s) for Noncancer Endpoints of Substances of
 Potential Concern                                            vm-33
 Components of Risk Descriptors and High-end Subgroups
 Evaluated in the Sensitivity Analysis                           VTfl-34
 Estimated Total Inhalation Cancer Risks for Substances of
 Potential Concern                                            VEI-35
 Estimated Total Inhalation Noncancer Hazard Indices for
 Substances of Potential Concern                               Vm-36
 Comparison of Predicted Acid Gas and Paniculate flatter
 Concentrations with NAAQS                                  Vm-37
 Estimated Cancer Risks Due to Exposure from Indirect
 Pathways                                                    Vm-38
 Estimated Hazard Indices Due to Exposure from Indirect
 Pathways                                                    VID-39
 Average Cancer Risks for an Adult Subsistence Farmer           VHJ-40
 Average Noncancer Hazard Indices for an Adult Subsistence
 Farmer                                                     VCD-41
 Chemical-specific Carcinogenic Risks for the Adult
 Subsistence Farmer in Subarea El (Area Average)                Vffl-42
 Chemical-specific Noncarcinogenic Hazard Indices for the
 Adult Subsistence Fanner in Subarea El (Area Average)          Vffl-45
 Estimated  Cancer Risks Due to Exposure from Direct and
 Indirect Pathways                                             VIH-47
 Estimated  Hazard Indices Due to Exposure from Direct and
 Indirect Pathways                                             VHI-48
 Comparison of Average and High-End Cancer Risks and
 Noncancer Hazard Indices for an Adult Subsistence Fanner in
 Subarea El                                                  VTfl-49
 Comparison of Average and High-End Cancer Risks and
 Noncancer Hazard Indices for a Subsistence Fanner  Child in
 Subarea El                                                  Vm-50
Input Values for the ffiUBK Lead Model                        VDI-51
Estimated Total Cancer Risks and Hazard Indices for
Subsistence Fishing (Average for Subareas and Location of
Maximum  Concentration)                                      Vm-52
Estimated Total Cancer Risks and Hazard Indices/for Deer
Hunting (Average for Subarea and Location of Maximum
Concentration)                                                Vffl-53
Volume V

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                                    TABLES
                                     (continued)
 Table VEI-19



 Table VHI-20

 Table Vm-21

 Table VHI-22

 Table VHI-23

 Table Vm-24


 Table VHI-25


 Table Vffl-26


 Table VHI-27
Table Vffl-28
Table Vm-29

Table IX-1

Table IX-2
Table DC-3
Table DC-4
 Estimated Total Cancer Risks and Hazard Indices for
 Consumption of Fruits and Vegetables from Residential Home
 Garden (Average for Subarea and Location of Maximum
 Concentration)                                                vm-54
 Estimated Cancer Risks for Infant Ingestion of Breast Milk
 (Average for Subarea and Location of Maximum Concentration)   VIQ-55
 Estimated Subarea Population Age Distribution for Residents
 and Farmers                                                  Vm-56
 Summary of Total Estimated Cancer Risks (Direct and Indirect)
 for Residents and Farmers                                     Vni-57
 Estimated Additional Cancer Cases Due to WTI Facility
 Emissions                                                    VTU-58
 Average Concentration Cancer Risks and Noncancer Hazard
 Indices for Fugitive  Organic Vapor Emission Sources at the
 WTI Facility                                                  Vm-59
 Total Cancer  Risks and Noncancer Hazard Indices at Location of
 Maximum Off-site Concentration  for Individual Fugitive
 Emissions Sources at the WTI Facility                           Vm-60
 Area Average and Maximum Location Cancer Risks and
 Noncancer Hazard Indices for Inhalation Exposure to
 Fugitive Ash  Emissions                                        Vm-61
 Area Average and Maximum Location Cancer Risks and
 Noncancer Hazard Indices for Indirect Exposure to
 Fugitive Ash  Emissions                                        VTTI-62
 Key Assumptions for Chapter VHI (Risk Characterization)         Vm-63
 Relative Concentrations of Selected Metals and Organic
 Compounds in Cows' Milk                                     Vm-64
 Summary of Typical Values and Ranges of Input Parameters
 Evaluated in Sensitivity Analysis                                 DC-31
 Summary of Sensitivity Analysis Results                          IX-38
Probability Distributions for Influential Parameters                 IX-42
Key Assumptions for Chapter DC  (Uncertainty Analysis)            DC-44
Volume V

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                                     FIGURES
  Figure VII-1      Approximate Locations of Farms Identified in the Beaver
                  Valley Power Station Survey with Beef Cattle or Dairy Cows       VTI-47
  Figure VII-2      Number of Dairy Farms by ZIP Code in Vicinity of the WTI
                  Facility                                                       VII-48
  Figure VTJ-3      Subareas Within Risk Assessment Study Area                     VH-49
  Figure VII-4      Location of Fugitive Emission Sources and Quadrants
                  Used to Evaluate Average Fugitive Emission Risks                 VH-50
  Figure Vffl-1     Probability Density Function for Childhood Exposure
                  to Lead Emitted from the WT1 Facility                         VIH-65
  Figure VHI-2     ZIP Code Boundaries in the Vicinity of the WIT
                  Incinerator Facility                                           Vffl-66
  Figure VEI-3     Comparison of Surrogate Chemical Selection Process
                  and Cancer Risks                                             Vm-67
Volume V

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                                APPENDICES
V-l          Summary of Log K^ Values
V-2          Physical/Chemical Parameter Values and Toxicity Values Used in Selection of
             Surrogate Organic Chemicals (Stack Emissions)
V-3          Physical/Chemical Values Used to Estimate Partitioning onto Panicles
V-4          Physical/Chemical Parameter Values and Toxicity Values Used in Selection of
             Surrogate Organic Chemicals (Fugitive Emissions)
V-5          Evaluation of Additional High-end Subgroups
V-6          Evaluation of Residential Exposure to Locally Caught Fish
V-7          Fate and Transport Model Equations and Parameter Values
V-8          Estimation of Exposure Factors
V-9          Review of USDA Milk Marketing Data
V-10         Milk Production by ZIP Code and Farm Size
V-ll         Estimation of Environmental Media Concentrations
V-l2         Estimation of Average Cancer and Noncancer Exposure Dose (LADD and
             ADD) for Subsistence Farmer in Subarea El
V-l3         Estimation of Maximum Cancer and Noncancer Exposure Dose (LADD and
             ADD) for Subsistence Farmer in Subarea El
V-l4         Estimation of Inhalation Cancer Risks and Hazard Quotients
V-l 5         Estimation of Cancer Risks and Hazard Indices for Indirect Exposure Pathways
             for Subsistence Farmer in Subarea El
V-l6         Exposure Pathway Cancer Risks and Hazard Indices
V-l7         Estimation of High-end Cancer Risks and Hazard Quotients for Subsistence
             Farmer and Child in Subarea El
V-l8         Estimation of Cancer Risks and Hazard Quotients for Subsistence Fisher and
             Local Deer Hunter
V-l9         Estimation of Population Risk
V-20         Estimation of Cancer Risks and Hazard Quotients Resulting from Fugitive
             Emissions
V-21         Summary of Input Parameters Used in Uncertainty Analysis
Volume V

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                                I.  INTRODUCTION
 A.   Overview of Volume V
      The Human Health Risk Assessment (HHRA) portion of the WTI Risk Assessment
 involves the integration of information about the facility with site-specific data for the
 surrounding region and population to characterize the potential human health risks due to
 emissions from the facility.  The estimation of human health risks is comprised of the
 following general steps: 1) identification of substances of potential concern; 2) estimation of
 the  nature and magnitude of chemical  releases from the WTI facility; 3) prediction of the
 atmospheric transport of the emitted contaminants; 4) determination of the types of adverse
 effects associated with  exposure to the substances of potential concern (referred to as hazard
 identification), and the  relationship between the level of exposure and the  severity of any
 health effect (referred to as dose-response assessment); 5) estimation of the magnitude of
 exposure (referred to as exposure  assessment);  and 6) characterization of the health risks
 associated with exposure (referred to as risk characterization).
      Volume HI of the  WTI Risk  Assessment identifies the chemicals that may be released
 from the WTI facility, both from the incinerator stack and from fugitive sources (step 1).
 These chemicals  (referred to as substances of potential concern)—which include metals,
 dioxins/furans, products of incomplete combustion, acid gases,  and paniculate matter—are
 summarized in Tables 1-1  and 1-2 for substances emitted from the stack and for fugitive
 emissions, respectively. Estimates of chemical-specific emission rates and the prediction of
 atmospheric concentrations and deposition of the substances of potential concern in the
 vicinity of the site (steps 2 and  3) are provided  in Volumes HI and IV, respectively.  Using
 this  information,  Volume V describes the  techniques used in partitioning the substances of
 potential concern into different environmental compartments  (e.g., soil, vegetables, etc.),
 calculating human exposure, and characterizing  health risks to individuals and population
 subgroups living and working in the vicinity of  the WTI facility.  In addition, within each
 chapter of the HHRA, a summary  of the sources of uncertainty and a qualitative discussion
 of these uncertainties is  provided, with a more detailed, quantitative analysis of uncertainties
 and the effect on  estimated risks provided  following the risk  characterization chapter.
     The approach used in the HHRA is designed to provide estimates of:  (1) individual risk
 based on central tendency  exposure (within subareas surrounding the facility) and at
 maximum points within  each subarea; (2) risks to highly exposed or susceptible subgroups of
Volume V

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the population (e.g., subsistence farmers and school children); (3) risks associated with
specific activities that may result in elevated exposures (e.g., subsistence fishermen and deer
hunters); and (4) population risk. In addition, for those subgroups of the population  that are
estimated to be more highly exposed, a  sensitivity analysis is conducted to evaluate potential
variabilities in exposure (e.g., "high-end" exposure).
     The estimation of risks is achieved by subdividing the area most affected by emissions
from WTI into subareas, and identifying subgroups to completely characterize the population
in the area.  In doing so, this approach allows for the estimation of risk to specific segments
of the population taking into consideration activity patterns, number of individuals, and actual
locations of individuals in these subgroups with respect to the site.
     The methodologies used in  estimating exposure and risks to identified subgroups in the
vicinity of the WTI facility are contained in  subsequent chapters and the associated
appendices as follows:

Chapter n:     Risk Assessment Methodology - which describes the steps and the guidance
               relied upon to conduct the HHRA;
Chapter HI:    Toxicity Assessment - in which measures of the human toxicity of substances
               of potential concern are identified;
Chapter IV:    Selection of Surrogate Chemicals - in which a subset of the organic
               compounds released from the facility are selected for evaluation in the HHRA
               in order to focus the assessment on the chemicals with the greatest potential
               for risk;
Chapter V:     Identification of Exposure Pathways and Populations - which identifies groups
               within the population living and working in  the vicinity of the facility who
               may be exposed to emissions from WTI and the potential routes by which an
               individual may be exposed;
Chapter VI:    Estimation of Environmental  Concentrations - which describes the techniques
               used to estimate the fate and  transport of site-related substances in the
               environment;
Chapter VTI:   Estimation of Human Exposure - which describes the methodology used to
               estimate exposure to subgroups of the population through exposure pathways
               identified in this  chapter;
Chapter Vni:   Human Health Risk Characterization - in which numerical estimates of
               carcinogenic risk and the potential for noncancer health effects are calculated
                                                                  £*
               for individual subgroups within the surrounding population, and for the
               population as a whole within the risk assessment study area;
Volume V

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 Chapter IX:    Uncertainty Analysis - in which uncertainties previously identified in the
                individual steps of the risk assessment process are summarized,  and to the
                degree possible, quantitatively evaluated;
 Chapter X:     Summary and Conclusions -  which presents the general conclusions of the
                HHRA for the WIT facility;  and
 Chapter XI:    References.
Volume V

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                                               TABLE 1-1
                           Substances of Potential Concern in Stack Emissions'
                              PICs and Residual Organic Compounds (174)
   Acenaphthene
   Acenaphthylene
   Acetaldehyde
   Acetone
   Acetophenone
   Acrolein
   Acrylonitrile
   Anthracene
   Benzaldehyde
   Benzene
   Benzoic acid
   Benzotrichloride
   Benzo(a)anthracene
   Benzo(a)pyrene
   Benzo(b)fluoranthene
   Benzo(e)pyrene
   Benzo(g,h,i)perylene
   Benzo(j)fluoranthene
   Benzo(k)fluoranthene
   Benzyl chloride
   Biphenyl
   Bis(2-chloroethoxy) methane
   Bis(2-chloroethyl)ether
   Bis(2-chloroisopropyl)ether
   Bis(2-ethylhexyl)phthalate
   BromochJoromethane
   Bromodichloromethane
   Bromoethene
   Bromoform
   Bromomethane
   Bromodiphenylether, p-
   Butadiene* 1,3-
   Butanone, 2- (MEK)
   Butylbenzylphthalate
   Carbon disulfide
   Carbon tetrachloride
   Chlordane
   Chloro-3-methylphenol, 4-
   Chloroacetophenone, 2-
   Chloroaniline, p-
   Chlorobenzene
   Chlorobenzilate
   Chloroe thane
   Chloroform
   Chloromethane
   Chloronaphthalcne, beta
 Chlorophenol, 2-
 Chlorodiphenylether, 4-
 Chloropropane, 2-
 Chrysene
 Cresol, m-
 Cresol, o-
 Cresol, p-
 Crotonaldehyde
 Cumene
 2,4-D
 4,4'-DDE
 Dibenz(a,h)anthracene
 Dibenz(a,h)fluoranthene
 Dibromo-3-chloropropane, 1,2-
 Dibromochloromethane
 Dichloro-2-butene, cis-1,4-
 Dichloro-2-butene, trans-1,4-
 Dichlorobenzene,  1,2-
 Dichlorobenzene,  1,3-
 Dichlorobenzene,  1,4-
 Dichlorobenzidine, 3,3'-
 Dichlorobiphenyl
 Dichlorodifluoromethane
 Dichloroethane, 1,1-
 Dichloroethane, 1,2-
 Dichloroethene, 1,1-
 Dichloroethylene, trans-1,2-
 Dichlorofluoromethane
 Dichlorophenol, 2,4-
 Dichloropropane, 1,2-
 Dichloropropene, cis-1,3-
 Dichloropropene, trans-1,3-
 Dietbylphthalate
 Dimethoxybenzidine, 3,3'-
 Dimethylphenol, 2,4-
 Dimethylphthalate
 Di-n-butylphthalate
 Di-n-octyl phthalate
 Dinitritoluene, 2,6-
 Dinitro-2-methylphenol, 4,6-
 Dinitrobenzene,  1,2-
 Dinitrobenzene,  1,3-
Dinitrobenzene,  1,4-
Dinitrophenol, 2,4-
Dinitrotoluene, 2,4-
Dioxane, 1,4-
 Ethyl methacrylate
 Ethylbenzene
 Ethylene dibromide
 Ethylene oxide
 Ethylene thiourea
 Fluoranthene
 Fluorene
 Formaldehyde  '
 Furfural
 Heptachlor
 Heptachlorobiphenyl
 Hexachlorobenzene
 Hexachlorobiphenyl
 Hexachlorobutadiene
 Hexachlorocyclohexane, alpha-
 Hexachlorocyclohexane, beta-
 Hexachlorocyclohexane, gamma-
  (a.k.a. Lindane)
 Hexachlorocyclopentadiene
 Hexachloroethane
 Hexachlorophene
 Hexane, n-
 Hexanone, 2-
 Hexanone, 3-
 Indeno( 1,2,3-cd)pyrene
 Isophorone
 Maleic hydrazide
 Methoxychlor
 Methylene bromide
 Methylene chloride
 Methylnaphthalene, 2-
 Methyl-tert-butyl ether
 Methyl-2-Pentanone, 4-
 Monochlorobiphenyl
 Naphthalene
 Nitroaniline,  2-
 Nitroaniline,  3-
 Nitroaniline,  4-
 Nitrobenzene
 Nitrophenol,  2-
 Nitrophenol,  4-
 N-Nitroso-di-n-butylamine
N-Nitroso^di-n-propylamine
N-Nitrosodiphenylamine
Nonachlorobiphenyl
Octachlorobiphenyl
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TABLE 1-1 (continued)
. Substances of Potential Concern in Stack Emissions'
PICs
Pentachl orobenzene
Pentachlorobiphenyl
Pentachloronitrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Phosgene
Propionaldehyde
Pyrene
Quinoline
Quinone
Safrole
Dioxin Congeners (7)
2,3,7,8-TCDD
1, 2,3,7, 8-PeCDD
1.2,3,4,7,8-HxCDD
1, 2,3,6, 7,8-HxCDD
1,2,3,7,8,9-HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD

Aluminum
Antimony
Arsenic
Barium
Beryllium
and Residual Organic Compounds (174)
Styrene
Tetrachlorobenzene, 1,2,4,5-
Tetrachlorobiphenyl
Tetrachloroethane, 1,1,1,2-
Tetrachloroethane, 1,1,2,2-
Tetrachloroethene
Tetrachlorophenol, 2,3,4,6-
Toluene
Toluidine, o-
Toluidine, p-
Trichloro-l,2,2-TFE, 1,1,2-
Trichlorobenzene, 1,2,4-
Furan
2,3,7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4,7, 8-PeCDF
1,2,3,4,7, 8-HxCDF
1,2,3,6,7,8-HxCDF
Trichlorobiphenyl
Trichloroethane, 1.1.1-
Trichloroethane, 1.1.2-
Trichloroethene
Trichlorofluoromethane
Trichlorophenol, 2,4.5-
Trichlorophenol, 2,4.6-
Trichloropropane, 1.2.3-
Vinyl acetate
Vinyl chloride
Xylene, m-
Xylene, o-
Xylene, p-
Congeners (10)
1,2,3,7,8,9-HxCDF
2,3,4,6,7, 8-HxCDF
1,2,3,4,6,7,8-HpCDF
1,2,3,4,7, 8,9-HpCDF
OCDF
Metals (15)
Cadmium
Chromium (hexavalent and
trivalent)
Copper
Lead
Mercury (inorganic and organic)
Nickel
Selenium
Silver
Thallium
Zinc
Acid Gases (3)
Hydrogen chloride
Total nitrogen oxides (NOJ
Total sulfur oxides (SOJ
Paniculate Matter (2)
Respirable (PM10)
Total
Notes.
The number of substances in each group is shown in parentheses
« - Substances of Potential Concern list developed as described 1.1 Volume ffl
TFE - trifiuoroethane MEK - methyl ethyl ketone
CDD - chlorodibenzo-p-dioxin PMW - paniculate matter < 10 microns
CDF - chlorodibenzofuran
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                                               TABLE 1-2
                                 Fugitive Substances of Potential Concern
                                 Fugitive Organic Vapor Emissions* (96)
   Acetone
   Acetonitrile
   Acetophenone
   Acetylaminofluorene, 2-
   Acrylonitrile
   Alcohols
   Aliphatic hydrocarbons
   Aniline
   Benzene
   Benzenedicarboxylic acid, 1,2-
   Benzidine
   Benzoquinone, p-
   Benzo(a)pyrene
   Butanol
   Butanone, 2-
   Butyl acetate
   Calcium chromate
   Carbon
   Carbon disulfide
   Carbon tetrachloride
   Chlorobenzene
   Chloroform
   Chlorinated paraffin, oil,  wax
   Chrysene
   Creosote (coal tar)
   Cresol
   Crotonaldehyde
   Cumene
   Cyclohexane
   Cyclohexanone
   Dibenz(a,h)anthracene
   Dibromoethane, 1,2-
Dichlorobenzene
Dichlorodifluoroethane
Dichlorodifluoromethane
DichJoroethane, 1,1-
Dichloroethene
Diethyl stilbestrol
Diethylphthalate
Dimethyl sulfate
Dimethylamine
Dimethylbenzidine, 3,3'-
Dimethylhydrazine
Dimethylphenol, 2,6-
Dimethylphthalate
Dinitrotoluene
Dioxane,  1,4-
Epichlorohydrin
Ethanol
Ethoxyethanol, 2-
Ethyl acrylate
Ethylbenzene
Fluoranthene
Formaldehyde
Formic acid
Furfural
Heptane
Hydrazine
Indeno( 1,2,3-cd)pyrene
Isobutanol
Isopropanol
Isosafrole
Maleic anhydride
Methanol
 Methyl methacrylate
 Methylbutadiene. 1-
 Methylcholanthrene, 3-
 Methyl isobutyl ketone
 Naphthalene
 Naphthylamine, 1-
 Naphthylamine, 2-
 Nitrobenzene
 Nitrophenol, 4- "
 Nitropropane, 2-
 N-nitrosodiethanolamine
 N-nitrosodiethylamine
 N-nitrosodi-n-butylamine
 N-nitrosopyrolidine
 Phenol
 Phthalic anhydride
 Picoline, 2-
 Pyridine
 Resorcinol
 Tetrachlorobenzene, 1,2,4,5-
 Tetrachloroethane, 1,1,1,2-
 Tetrachloroethene
 Tetrahydofuran
 Toluene
 Toluene diisocyanate
 Toluenediamine
 Trichloro-l,2,2,-TFE. 1,1,2-
Trichlorobenzene
Trichloroethane, 1,1,1-
Trichloroethene
Trichlorofluoromethane
Xylene
                                       Fugitive Ash Emissions'1 (8)
              Arsenic
              Barium
              Cadmium
                Lead
                              Nickel
                             Selenium
                              Silver
                             Cyanide
  Notes:
  The number of substances in each group is shown in parentheses
  a -      Developed from list of "pumpable" waste streams expected at WTI during first year of operation. These substances
          represent approximately 90 percent of the total pumpable waste stream. Pumpable waste stream constituents list developed
          as described in Appendix HI-1
  b -      Based on metals detected in fly ash samples collected by WTI (1995).                 '
  TFE -   trifluoroethane
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                  H.  RISK ASSESSMENT METHODOLOGY
     The HHRA for the WIT facility consists of the evaluation of potential human health
 risks associated with exposure to incinerator stack and fugitive emissions produced during
 routine operation of the facility.  A brief introduction to the general risk assessment process
 and recent U.S.  EPA guidance relevant to the assessment of risks from indirect exposure to
 incinerator emissions is presented in the following sections.

 A.  The Risk Assessment Process
     The foundation for the risk assessment methods described in this report is consistent
 with well-established chemical risk assessment principles and procedures developed for the
 regulation of environmental contaminants (NRC 1983, OSTP 1985, U.S.  EPA 1986a,b).
 Application of these guidelines and principles provides a consistent process for evaluating
 and documenting potential health risks associated with environmental exposures.
     The risk assessment process used by federal regulatory agencies and applied in this
 assessment is essentially that described by the National Research Council  (NRC 1983), and
 consists of the following four components:

     •    Hazard identification, in which the chemical substances of concern in emissions
          from the facility are identified and data relevant to the toxic properties of these
          substances are compiled, reviewed, and evaluated;

     •    Dose-response evaluation, in which the relationship between dose and response is
          evaluated for each chemical of potential concern to derive toxicity values that can
          be  used to estimate the incidence of adverse effects occurring at different exposure
          levels;

     •    Exposure assessment, in which potential exposure pathways are identified and
          measures  of chemical exposure (e.g., concentrations for the various environmental
          media,  or doses) are estimated for the potential exposure pathways,  based upon
          various exposure assumptions and the characteristics of the population receiving
          the exposure;  and,
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• Risk characterization, in which numerical estimates of risk are calculated for each
substance by each potential route of exposure using the toxicity information and
the exposure estimates.

In addition to the steps listed above, the HHRA characterizes uncertainty associated
with each step of the process and includes an analysis of the potential effects of the
individual sources of uncertainty as part of the risk characterization.
It should also be noted that in the HHRA, the first two steps of the risk assessment
process, hazard identification and dose-iesponse assessment, are simplified by using toxicity
information compiled by U.S. EPA. This information is typically used in conducting risk
assessments where a significant number of common environmental contaminants are being
evaluated. The combination of these steps in this assessment is referred to as the Toxicity
Assessment.

B. Other U.S. EPA Guidance Documents
In conducting the HHRA, various sources of U.S. EPA guidance are relied upon that
are specific to incineration or provide recent guidance on some aspect of the risk assessment
process (e.g., exposure assessment). As previously emphasized, U.S. EPA guidance is used
in conjunction with site-specific data and information to the extent possible.

• The primary source of U.S. EPA guidance for conducting the HHRA is the
Methodology for Assessing Health Risks Associated with Indirect Exposure to
Combustor Emissions, Interim Final (U.S. EPA 1990a).

• In addition, the Addendum to Methodology for Assessing Health Risks Associated
with Indirect Exposure to Combustor Emissions, External Review Draft (U.S. EPA
1993a) that is presently undergoing U.S. EPA revision in response to an external
peer review by the U.S. EPA Science Advisory Board (SAB) is relied upon for the
analysis.

Other recent U.S. EPA guidance that is relied upon to complete this risk assessment
include the Revised Draft Implementation Guidance for Conducting Indirect Exposure
Analysis at RCRA Combustion Units, (U.S. EPA 1994a), the Guidance on Risk
Characterization for Risk Managers and Risk Assessors (U.S. EPA 1992a), the Guidance for
•**
Risk Characterization (U.S. EPA 1995a), and the Guidelines for Exposure Assessment (U.S.
EPA 1992b), which were developed by U.S. EPA to clarify and refocus the requirements for
a complete and balanced risk assessment. For example, the Guidelines for Exposure

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 Assessment provide a general outline of the possible methods that U.S. EPA recommends
 using in an exposure assessment, and identifies important issues concerning presentation of
 results (e.g., use of various risk descriptors) and uncertainties.
      Additional sources of guidance that are relied upon for the HHRA include: Exposure
 Factors Handbook (U.S. EPA 1990b), Dermal Exposure Assessment: Principles and
 Applications (U.S. EPA 1992c), Estimating Exposure to Dioxin-Like Compounds, Volume II:
 Properties, Sources, Occurrence and Background Exposure, Review Draft (U.S. EPA
 19945), Estimating Exposure to Dioxin-Like Compounds, Volume III: Site-specific Assessment
 Procedures,  Review Draft (U.S.  EPA 1994c), Guidance on Metals and Hydrogen Chloride
 Controls from Hazardous Waste Incineration (U.S. EPA 1989a), and other related risk and
 exposure assessment guidance documents.
      A Project Plan (U.S. EPA 19935) that descri5es the proposed methodology used in this
 assessment was previously developed and reviewed 5y an external peer review panel.  As
 noted earlier, recommendations made by the peer reviewers are incorporated into this
 assessment to the extent possible.
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ffl. TOXICITY ASSESSMENT
The toxicity assessment portion of the HHRA combines hazard identification and dose-
response assessment. The primary objectives of this step of the risk assessment process are
to identify the types of toxic effects associated with each substance of potential concern,
characterize the conditions (e.g., route, duration) of exposure under which these effects
might occur, and determine the relationship between the magnitude of human exposure and
the extent of adverse health effects. This relationship is represented through the use of
toxicity values relating to cancer or noncancer health endpoints.

A. Toxicity Assessment Methods
U.S. EPA has conducted toxicity assessments on many of the most frequently occurring
environmental chemicals and has developed toxicity values for use in risk assessment, based
on these analyses. Cancer and noncancer toxicity values for chemical substances are
published by U.S. EPA and are updated regularly (IRIS 1995; U.S. EPA 1994d). The
Integrated Risk Information System (IRIS) is an on-line data base maintained by U.S. EPA
that provides toxicity data for many commonly detected substances. A second source of
toxicity values is the Health Effects Assessment Summary Tables (HEAST) (U.S. EPA
1994d), which U.S. EPA also updates regularly. The procedures used by U.S. EPA in
evaluating toxicity studies to develop toxicity values are described below.

1. Carcinogenic Effects
Substances classified by U.S. EPA as potentially carcinogenic are considered by
many scientists to pose a finite cancer risk at all exposure levels. In evaluating cancer
risks, therefore, a "no-threshold" assumption is applied. It should be noted that the no-
threshold assumption may not apply for some classes of carcinogens that act through a
mechanism that requires a threshold dose to be exceeded prior to initiation of the
carcinogenic process. For purposes of this assessment, U.S. EPA's no-threshold
assumption is conservatively assumed for all chemical carcinogens.
A two-step evaluation is used in assessing the carcinogenic potential of a chemical.
The first step involves evaluating the likelihood that the substance is a human
carcinogen (i.e., a weight-of-evidence assessment), and the second step involves
defining the quantitative relationship between dose and response (i.e., development of a
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slope factor). In the first step, U.S. EPA classifies a chemical into one of five groups
that indicate the likelihood that the chemical is a human carcinogen, based on the
weight of evidence from human and animal investigations as follows:

• Group A chemicals are classified as human carcinogens;
• Group Bl chemicals are probable human carcinogens with limited human data
available and group B2 chemicals are probable human carcinogens with
sufficient evidence in animals and inadequate or no evidence in humans:
• Group C chemicals are possible human carcinogens; and
• Group D chemicals are not classifiable as to human carcinogenicity.

Those chemicals that are determined to be known, probable, or potential human
carcinogens are further evaluated. The outcome of the second part of the evaluation is
the development of the slope factor (SF), which is a measure of the potency of the
carcinogen. The SF represents the upper 95 percent confidence limit on the linear
component of the slope of the tumorigenic dose-response curve in the low-dose (low-
risk) region. The SF is an upper bound estimate of the likelihood that a response will
occur per unit intake of a chemical over a 70-year lifetime, and is derived by applying a
mathematical model to extrapolate from the relatively high doses administered to
experimental animals or experienced by persons in the workplace to the lower exposure
levels expected for human contact in the environment. A number of low-dose
extrapolation models have been developed; U.S. EPA generally uses the linearized
multistage model in the absence of adequate information to support some other model.
The linearized multistage model is believed to be conservative, i.e., is likely to
overpredict the true SF for a chemical.

2. Noncarcinogenic Effects
The basic approach used by U.S. EPA in developing toxicity values for
noncarcinogenic effects of substances is based on the belief that some minimum
(threshold) exposure level must be reached before the effect will occur, i.e., that
protective mechanisms exist that must be overcome before an adverse health effect can
occur. The estimated level of daily human exposure below which it is unlikely that
deleterious effects will result is known as the Reference Dose (RfD). RfD values are
reported in milligrams of chemical per unit body weight per day (mg/kg/d). Unless
adequate human data are available, U.S. EPA develops an RfD value based on data
from experimental animals. If data from several animal studies are available, U.S.
EPA first seeks to identify the animal model that is most biologically relevant to
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humans (e.g., similar metabolism of the substance). In the absence of information that
identifies a given animal model as clearly most relevant, U.S. EPA assumes that
humans are at least as sensitive to the substance as the most sensitive animal species
tested. Accordingly, U.S. EPA selects the study using the most sensitive species tested
and the most sensitive endpoint measured as the critical study upon which the RfD is
based (U.S. EPA 1989b).
From this critical study, the experimental exposure representing the highest dose
level tested at which no adverse effects were demonstrated (the no-observed-adverse-
effect level, NOAEL) is identified. In selecting the NOAEL as the basis for the RfD.
the assumption is made that if the critical toxic effect is prevented from occurring, then
all toxic effects are prevented. The NOAEL is to be distinguished from the no-
observed-effect level (NOEL), which corresponds to the exposure level at which no
effect at all is observed; whereas, the NO AFT is the level at which no effect considered
to be of lexicological significance is observed. In some studies, only a lowest-
observed-adverse-effect level (LOAEL) is available. The use of a LOAEL in deriving
an RfD requires the use of an additional uncertainty factor, as described below (U.S.
EPA 1989b).
The RfD is derived from the NOAEL or LOAEL for the critical toxic endpoint by
dividing the NOAEL or LOAEL by one or more uncertainty factors. These factors
generally are multiples of 10, with each factor representing a specific area of
uncertainty in the extrapolation from the available study data. For example, a 100-fold
uncertainty factor is typically used when the RfD is based on results from long-term
animal studies. This factor of 100 incorporates an uncertainty factor of 10 to account
for variation in sensitivity in the human population and another uncertainty factor of 10
to account for interspecies variability between humans and experimental animals.
Additional modifying factors ranging from 1 to 10 may be applied to reflect qualitative
judgements about limitations or uncertainties in the critical study or in the data base as a
whole that are not explicitly addressed by the standard uncertainty factors (U.S. EPA
1989b). Thus, since the RfD is intended to be adequately protective of sensitive
individuals, application of the RfD to the general population is conservative.
Reference Concentration (RfC) values have been developed by U.S. EPA for the
assessment of non-carcinogenic effects from inhalation exposures. RfC values are
reported as air concentrations in units of mass of chemical per unit volume of air (e.g.,
mg/m3). In this assessment, the potential for adverse effects as a result of inhalation
exposure is estimated by comparing exposure concentrations to a' fixed fraction of the
RfC. Based on U.S. EPA guidance (U.S. EPA 1989c), a fixed fraction of 25 percent
of the threshold toxicity value (RfC) is allocated for direct inhalation exposure. The
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     remaining 75 percent of the threshold is allocated to background and other exposures.
     This is likely a conservative approach to estimating the potential for noncancer health
     effects from inhalation exposure, thus ensuring that such risks are likely not
     underestimated.  The acceptable concentration calculated in this manner is defined as
     the reference air concentration (RAC), which is determined from the inhalation RfC. if
     available, or calculated from the oral reference dose (RfD).
          For toxic substances for which verified inhalation RfCs are not available,  the RAC
     is calculated from the oral reference dose (RfD) as recommended in the incinerator
     controls guidance document (U.S. EPA 1989c) and the final rule for boilers and
     industrial furnaces (U.S. EPA 1991):
                                    -
-------
      dioxin (2,3,7,8-TCDD), which is generally believed to be the most toxic form (U.S.
      EPA 1994b).  Each congener is assigned a value, referred to as a toxicity equivalency
      factor (TEF), corresponding to its toxicity relative to 2,3,7,8-TCDD (i.e., 2.3.7.8-
      TCDD has a TEF of 1.0 and other dioxin and furan congeners have TEFs between zero
      and 1.0).  Although various groups and organizations have developed TEF schemes, the
      U.S. EPA-recommended approach (U.S. EPA 1994b) is used in this risk assessment.
      This approach is the same as the internationally accepted approach given in  the North
      Atlantic Treaty Organization, Committee on the Challenges of Modern Society
      (NATO/CCMS 1988).  The TEFs for dioxin and furan congeners considered in this
      assessment are presented in Table ffl-2.
          Of the 210 possible congeners of the chlorinated dioxins and furans, only the 17
      congeners having chlorine substituents in the 2, 3,  7, and 8 positions are generally
      regarded as displaying dioxin-like toxicity (Table ffl-2). As mentioned above, the
      cancer slope factors for dioxin and furan compounds other than 2,3,7,8-TCDD are
      derived by the assignment  of TEF values which compare the toxicity of the toxic
      congeners to that of 2,3,7,8-TCDD. For 2,3,7,8-TCDD, the cancer slope factor  is
      based on actual experimental evidence in rodents.  For the other 16 toxic congeners, the
      toxic potency compared to 2,3,7,8-TCDD is based  upon receptor binding studies or a
      sensitive measure of receptor binding, namely induction of Aryl Hydrocarbon
     Hydroxylase (AHH) enzyme activity.  These TEFs have been developed based upon the
     activity of these compounds in short-term toxicity assays that are considered  predictive
     of their ability to cause cancer in long-term carcinogenicity studies in experimental
     animals.  Consequently, the cancer slope factors (derived from the TEF values) for
     these 16 toxic congeners are less certain than the cancer slope factor for 2,3,7,8-TCDD.
          In accordance with U.S. EPA guidance (U.S.  EPA 1994b,c), the individual dioxin
     and furan congeners are assessed separately throughout the exposure assessment
     process.  This involves the estimation of congener-specific emission rates, followed by
     the evaluation of each congener for partitioning into various environmental media.  This
     approach  is adopted due to the important differences between dioxin and furan
     congeners  in the fate and transport properties needed to  estimate exposures through the
     food chain pathways (U.S.  EPA  1994b,c; Washburn 1991; McLachlan 1993).  The
     TEFs are applied in the final step of the risk assessment process, in estimating potential
     health risks.
          In addition to the potential for dioxins to cause cancer, there is also concern for
     the potential noncancer effects from these chemicals.  U.S. EPA concludes that
     adequate evidence exists to suggest that exposure to 2,3,7,8-TCDD and related
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     dioxin-like compounds results in a broad spectrum of effects in animals, some of which
     may occur in humans (U.S. EPA 1994h).
          This conclusion is based upon results from epidemiology studies in human
     populations, experiments in laboratory animals, and ancillary  experimental studies.  The
     effects induced will likely range from adaptive changes at or near background levels of
     exposure to adverse effects with increasing severity as exposure levels increase above
     background levels.  Enzyme induction, alterations in hormone levels  and indicators of
     altered cellular function are examples of effects of currently unknown significance:  they
     may or may not be early indicators of toxic response. Because the threshold levels for
     exposure to 2,3,7,8-TCDD and dioxin-like compounds below  which toxic effects are not
     observed has not been established, the U.S. EPA does not currently list RfD or RfC
     values for dioxin-like compounds.
          The deduction that humans could respond to exposures to 2,3,7,8-TCDD and
     dioxin-like compounds  with adverse non-cancer effects is based on the fact that these
     compounds impact cellular regulation at a fundamental molecular level in a diverse
     variety of animal species which have been shown to respond with adverse effects.  In
     addition,  similar impacts on cellular regulation have been demonstrated in human cells
     in experimental cell  culture.
          It is well  known that individual animal species vary in their sensitivity to exhibit
     different effects due to exposure to 2,3,7,8-TCDD.  However, the available evidence
     indicates that humans most likely fall in the middle of the range of sensitivity for
     individual effects among animals rather than at either extreme. Thus, humans do not
     appear to be either extremely sensitive to or extremely insensitive to the individual
     effects of 2,3,7,8-TCDD and dioxin-like compounds.
          In general, biochemical, cellular and organ-level  effects have been observed in
     experiments in which only 2,3,7,8-TCDD was studied. Specific data on the effects of
     other dioxin-like homologues such as the pentachlorinated and hexachlorinated dioxins
     and furans are  generally not available.  However, as mentioned previously, dioxin-like
     compounds exhibit the common property of binding to the intracellular Aryl
     Hydrocarbon Hydroxylase receptor.  Based upon differences in receptor binding
     capacity, toxicity equivalence factors (TEFs) have been developed for the 17 dioxin and
     furan congeners with chlorine  substituents  in the 2,3,7, and 8  ring positions.  The TEF
     for 2,3,7,8-TCDD is one; the  TEFs for the 16 other congeners are a  fraction of this
     value (i.e., between zero and 1.0).
          Greater uncertainty exists with respect to the extent of non-cancer effects of the 16
     other congeners as compared to those of 2,3,7,8-TCDD due to the very limited amount
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      of toxicology testing of these congeners.  Hence greater uncertainty is associated with
      the TEFs of these congeners as compared to the TEF for 2,3,7,8-TCDD.
          The draft dioxin reassessment issued by the Agency in 1994 (U.S. EPA 1994h)
      concludes that it is inappropriate to develop a reference dose for dioxins because dioxins
      are persistent compounds in the environment and because pre-existing background
      exposures to dioxins are not low compared to incremental environmental exposures.
      For most compounds for which reference doses are applied, the compounds are not
      persistent, and background exposures are generally very low and not taken into account.
      Therefore, the draft dioxin reassessment has  concluded that it is not appropriate to use
      the reference dose approach in evaluating incremental exposures to dioxins.
          Based upon the findings of the draft dioxin reassessment, the EPA Office of
      Research and Development and Office of Solid Waste and Emergency Response have
      recommended using a "margin of exposure" approach for estimating potential non-
      cancer health effects arising from incremental exposures to dioxins.  Using this
      approach, one determines the ratio of the estimated daily dose of dioxins from a
     particular source (in this case, the long-term operations of the WTT incinerator) to the
     average daily intake of dioxins in the general population from existing sources, which is
     between 1 and 3 pg/kg-day in the United States and other industrialized nations from
     existing sources (U.S. EPA 1994h).
          To determine the daily exposure from the WTI incinerator, the individual TEF
     values for each dioxin and furan congener were applied to the estimated total
     incremental dose of each congener for the most highly exposed individual.  This
     resulted in the calculation of a toxic equivalent (TEQ) dose for each congener; the sum
     of the TEQ values for each of the congeners resulted in the total TEQ dose from
     operation of the WTI incinerator.  The ratio of this incremental dose to the background
     dose of 1-3 pg/kg-day represents the margin of exposure to dioxins.
         In this risk assessment, the individual TEF values for each dioxin and furan
     congener are applied to the estimated total incremental exposure dose of each congener
     for the most highly exposed individual.  This results in the calculation of a toxic
     equivalent (TEQ) dose for each congener. The sum of TEQ values for each congener
     results in a total TEQ dose.  The total TEQ exposure dose due to operation of the WTI
     incinerator is compared to the expected background TEQ exposure dose for individuals
     living in the vicinity  of WTI, as estimated by U.S.  EPA (1994b).
                                                              **
     2.   Poly cyclic Aromatic Hydrocarbons (PAHs)
         The compounds benzo[a]anthracene, benzo[a]pyrene, benzofbjfluoranthene,
     benzo[k]fluoranthene, chrysene,  dibenzo[a,h]anthracene,  and indeno[l,2,3-cd]pyrene,
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     are considered to be carcinogenic by U.S. EPA. With the exception of cnrysene, the
     PAHs listed above are all known animal carcinogens.  U.S. EPA has derived an oral
     slope factor of 7.3 (mg/kg-day)'1 (IRIS 1995) for benzo[a]pyrene (BaP); however, the
     remaining carcinogenic PAHs have not been assigned carcinogenic toxicity values in
     IRIS because of the limitations of the cancer studies performed on these compounds.
          Until individual toxicity values are assigned, U.S. EPA (1993c) recommends an
     interim relative potency approach to determining carcinogenic potential based upon
     results in a group  of carcinogenicity studies in animals. The toxicity of each
     carcinogenic PAH is evaluated relative to the toxicity of BaP. The potency of BaP has
     been assigned a value of 1.0, which is equivalent to an oral slope factor of 7.3 (mg/kg-
     day)"1, and other PAHs have relative potencies between zero and one, as shown in Table
     ffl-3. Each of the PAHs considered in this assessment are evaluated separately with
     regard to estimating  stack emissions, modeling fate and transport in the environment.
     and quantifying human dose.  The relative potency  factors in Table ffl-3 are applied in
     the final step of the risk assessment process, in estimating potential health  risks.

     3.    Lead
          U.S. EPA does not currently  list an RfD or RfC for lead because a threshold level
     for exposure to lead  below which toxic effects are not observed has not been
     established.  Additionally, based upon findings that neurobehavioral effects have been
     observed  in children with blood lead levels below those that have caused carcinogenic
     effects in laboratory animals, a cancer SF has not be derived by U.S. EPA.  The
     Agency has relied  upon the neurological effects observed in children  as the sensitive
     endpoint for evaluating lead toxicity.  Consequently, U.S.  EPA has applied an
     uptake/biokinetic modeling approach, which evaluates potential risks  by predicting
     blood lead levels associated with exposure to lead.  The uptake/biokinetic model (U/BK)
     for lead was developed through the efforts  of U.S. EPA (1990c) and New  York
     University professors N.H. Harley and T.J. Kneip (Kneip  et al. 1983). It  integrates a
     number of assumptions about the complex exposure pattern and physiological handling
     of  lead by the body,  and has been validated at several sites where lead exposure data
     and human blood lead levels are available (U.S.  EPA 1990c). The U/BK model has
     been reviewed and recommended by the U.S. EPA  Science Advisory Board (SAB)
     (U.S. EPA 1992d).
          U.S. EPA has developed a  computerized version of the U/BK model  (version
     0.99d) that predicts blood  lead levels and distributions for children ages zero to seven
     years of age (U.S. EPA 1994e).  At present, as directed by U.S. EPA (1994e), it is not
Volume V
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     possible to apply the computer model to predict potential blood lead levels in adults.  In
     general, however,  children are more susceptible to lead exposures than adults as a result
     of higher soil ingestion rates and greater absorption from the gut,  in addition to
     nutritional variables and lower body weight. Thus, in this assessment, environmental
     concentrations of lead resulting from stack emissions are used, with the U/BK model, to
     predict the child blood lead levels.

     4.   Mercury
          Mercury can  exist in either organic or inorganic forms in the environment.
     Although emissions from the stack at the WTI facility are expected to be in an  inorganic
     form (as metallic mercury), it is possible that some portion of the  mercury is convened
     to organic forms (e.g., methylmercury) in the environment. The bioaccumulation
     potential of methylmercury may be as much as ten times greater than that of inorganic
     forms of mercury.  Based on recommendations by U.S. EPA in  its Report to Congress
     on mercury in the  environment (U.S. EPA 1994f), it is assumed that 25 percent of the
     mercury in aquatic environments is in the organic form.  Mercury  in air, soil,
     vegetation, and  animal products (with the exception of fish) is assumed to be entirely
     inorganic.

     5.   Nickel
          U.S.  EPA treats certain forms of nickel, including nickel carbonyl, nickel
     subsulfide,  and  nickel  refinery dust, as carcinogens. However, U.S. EPA, in the Final
     Rule for Burning of Hazardous Wastes in Boilers and Industrial Furnaces  (U.S. EPA
     1991), does not consider nickel emissions from hazardous waste  combustions units to be
     carcinogenic because the carcinogenic forms of nickel are not expected to  be present in
     the oxidizing environment of combustion units.   More recent data,  however, suggest
     other forms of nickel may be carcinogenic, and the International Agency for Research
     on Cancer (1ARC)  has classified "nickel and certain nickel  compounds" as probable
     human, inhalation carcinogens.  Therefore, to ensure that the potential inhalation cancer
     risks associated  with inhalation exposure to airborne nickel are not underestimated, this
     assessment evaluates nickel as an inhalation  carcinogen.

     6.  Chromium
         The oxidation state of chromium is a crucial issue in evaluating the toxicity of this
                                                                /••
     metal and the risks associated with exposure. Hexavalent chromium (Cr+6) is the most
     toxic valence state of chromium and has been shown to be a human carcinogen through
     inhalation exposure. Trivalent chromium, a commonly found less oxidized form of
Volume V
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     chromium, has not been shown to be carcinogenic in either humans or laboratory
     animals.  U.S. EPA (1990d,e) has indicated that chromium emitted from a combustion
     unit is not likely to be in the hexavalent form; however, sufficient evidence does not
     exist to reliably estimate the partitioning of chromium emissions into these two valence
     states. Therefore, the worst-case assumption that 100 percent of the facility chromium
     emissions are in the hexavalent form is adopted.

     7.   Acid Gases
          Exposure to acid gases may occur through the inhalation pathway. However, there
     are currently no U.S. EPA-verified inhalation toxicity values (e.g., RfC or SF values)
     for sulfur oxides or nitrogen oxides. Therefore, estimated air concentrations of these
     acid gases are compared in  this assessment to the National Ambient Air Quality
     Standards (NAAQS), which were developed by U.S. EPA to be protective of human
     health. The NAAQS for sulfur dioxide and  nitrogen dioxide are 100 /ug/m3 and 80
          3, respectively (40 CFR 50.4-50.12).
     8.   Partial late Matter
          There are currently no RfD, RfC, or SF values for either total particles or
     respirable particles (generally assumed to be particles with an aerodynamic diameter
     equal to or less than 10 micrometers,  or PM10).  In this assessment, estimated air
     concentrations of paniculate matter are compared to the NAAQS.  The annual average
     NAAQS for PM10 is 50 ng/m3 (40 CFR 50.4-50.12).

C.   Toxicity Assessment for Substances of Potential Concern in Fugitive Emissions
     Although the general methodology for assessing the toxicity of chemicals emitted from
fugitive sources does not differ from the methodology used for substances emitted from the
stack, a different list of chemicals may apply to emissions from fugitive sources.  As noted
previously, fugitive emissions occur from two types of sources resulting in two different
types of substances: volatile organic compounds (from four specific sources) and metals (in
ash).

     1.   Fugitive Organic Chemical Emissions
          Given their  volatile nature,  exposure to fugitive vapor emissions is expected to
     occur primarily through inhalation.  Therefore, the relevant inhalation toxicity values
     (e.g., RAC, inhalation SF) are compiled from IRIS (1995) and HEAST (U.S. EPA
Volume V
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      1994d), and are presented in Table ffl-4.  As indicated in Table ffl-4, for the chemicals
      with potential noncancer health effects, RACs are developed from the RfCs or from oral
      RfDs, based on a route-to-route extrapolation, as described earlier.

      2.   Fugitive Ash Emissions
           The evaluation of risks associated with fugitive ash emissions is conducted for
      exposure by inhalation and by indirect exposure pathways.  The relevant inhalation and
      oral toxicity values for the substances identified in ash samples from the WTI facility
      are summarized in Table ffl-5.

 D.   Uncertainties
      In the majority of risk assessments, as in this risk assessment, available scientific
 information is insufficient to provide a complete understanding of all the toxic properties of
 chemicals to which humans are potentially exposed. It is generally necessary, therefore, to
 infer these properties by extrapolating them from data obtained under other conditions of
 exposure, frequently in laboratory animals. In evaluating the toxicity of the substances
 considered in this assessment,  a number of assumptions are made.  Table ffl-6 summarizes
 the key assumptions used in this chapter. In addition to noting the key assumptions, Table
 ITJ-6 provides the basis for each assumption, and the direction and relative magnitude of the
 effect of each assumption on the overall estimated risks, as discussed in Volume n.
     Experimental animal data have been relied upon for many years by regulatory agencies
 and  other expert groups for assessing the hazards and safety of human exposure to chemicals.
 This reliance has been supported in general by empirical observations.  There may be
 differences in chemical absorption, metabolism, excretion, and toxic response, however,
 between humans and the species for which experimental toxicity data are generally available.
 Uncertainties associated with the characterization of chemical toxicity  in humans are also
 introduced as a result of the following (U.S. EPA 1989b):

     •    Using dose-response information from effects observed at relatively high exposure
          levels to predict effects that may occur following exposure to the much lower
          exposure levels expected from contact with the chemical in the environment;

     •    Using data from one route of exposure to predict effects from exposure via  other
          routes;

     •   Using dose-response data from  short-term or subchronic exposures to predict the
         effects following longer-term exposure; and

Volume V                               TTT^I 1
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     •    Using dose-response information from homogeneous animal populations or healths
          human populations to predict effects that may occur in the general population,
          including sensitive subpopulations.

     The methods for addressing these uncertainties in the lexicological assessment for
noncarcinogens and carcinogens are discussed below.

     1.    Uncertainties in the Characterization of the Toxicity of Carcinogens
          For many substances that are carcinogenic in animals, there is uncertainty  as to
     whether they are also carcinogenic in humans.  The Office of Science and Technology
     Policy (OSTP  1985) has observed the following:

          "...known human carcinogens,  with the single exception of arsenic,  are
          carcinogenic in appropriately conducted studies  in some animal system
          (arsenic has recently been reported to produce carcinomas of the
          respiratory tract in hamsters).  This does not  mean that all chemicals
          found carcinogenic in animals will turn out to be carcinogenic in
          humans.  Because of differences in the production of critical metabolites
          and because of other differences between species, a given carcinogen
          may not produce cancer in all species or in all strains of rodents."

          The finding that relatively few substances are known human carcinogens may  be
     due in part to the difficulty in conducting adequately  designed epidemiologic
     investigations in exposed human populations.  The available data in humans are  derived
     mainly from retrospective epidemiology studies of  workers exposed to multiple
     chemicals and at doses that can not be reliably quantified.
          As with RfD and RfC values, all U.S. EPA-verified slope factors in IRIS are
     accompanied by a weight-of-evidence classification, which is an indication of the
     likelihood that the agent is a human carcinogen.  This classification  is  based on  the
     completeness of the evidence that the agent causes  cancer in experimental animals and
     humans.  The strength of the evidence that a carcinogen is a potential  human  carcinogen
     is strengthened by such factors as the following: (1) greater number of tissue  sites
     affected by the agent; (2) carcinogenic response in more than one species, strain, and
     sex, and by multiple routes of exposure; (3) evidence of a clear-cut dose-response
     relationship as well as a high level of statistical significance of the  increased tumor
     incidence in treated compared to control groups; (4) dose-related shortening of the time-
     to-tumor occurrence or time to death with tumor; (5) dose-related increase in  the

Volume V                                -—  - -
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     proportion of tumors that are malignant; (6) a plausible biological mechanism of
     tumorigenicity; (7) similar carcinogenic properties exhibited by structurally-related
     compounds; (8) evidence of an association between exposure to the chemical of concern
     and an increased tumor incidence in human populations (U.S. EPA 1989b: U.S.  EPA
     1986a).
          Because of uncertainties associated with the measure of carcinogenic potency of a
     chemical in humans, U.S. EPA has adopted procedures in the calculation of slope
     factors that are generally conservative.  For example, in the absence  of data to the
     contrary, U.S.  EPA uses the biologically acceptable data set from long-term animal
     studies showing the greatest sensitivity (U.S. EPA 1986a).
          There are several mathematical models available to derive low-dose unit risks from
     high exposure levels used in experimental studies.  No single model is  recognized as the
     most appropriate for low-dose extrapolation.  The model generally used by U.S.  EPA is
     the linearized multistage model, which generally provides the most conservative
     estimate of risk at low doses (i.e., highest risk per unit dose).  The procedure employed
     by U.S. EPA is also to use the 95 percent upper confidence limit on  the slope of the
     dose-response curve estimated by the linearized multistage model. According to U.S.
     EPA (1989b), use  of the 95 percent upper confidence limit value, rather than the unit
     risk that represents the maximum likelihood estimate, provides an estimate of the upper
     boundary on risk.  U.S. EPA (1986a) has also emphasized "that the linearized
     multistage model leads to a plausible upper limit to the risk that is consistent with some
     proposed mechanisms of carcinogenesis.  Such an estimate, however, does not
     necessarily give a realistic prediction of the risk.  The true value of the risk is
     unknown, and may be as low as zero."

     2.  Uncertainties in the Characterization  of the Toxicity of Noncarcinogens
         To adjust for uncertainties such as those discussed above,  U.S. EPA and other
     regulatory agencies typically base the RfD or RfC (or other expression  of the acceptable
     daily intake) for noncarcinogens on the most sensitive animal species, i.e., the species
     that experiences adverse effects at the lowest dose.  This dose is then  adjusted by the
     use of uncertainty and modifying factors to compensate for various sources of
     uncertainty in the underlying toxicity data. The resulting toxicity factor incorporates a
     substantial margin of safety, although the actual magnitude of this safety margin cannot
     be quantified with any certainty.
         For all verified RfD and RfCs, U.S. EPA does provide in IRIS a qualitative
     statement of the confidence that the evaluators have in the RfD or RfC  itself, in the
     critical study upon which the RfD or RfC is based, and in the overall data base.
Volume V
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     3.   Uncertainties Associated with Route-to-route Extrapolation
          U.S. EPA guidance for hazardous waste incinerators (U.S. EPA 1989a) suggests
     that where a verified oral RfD has been developed by U.S. EPA but there is no verified
     RfC for that substance, the RfD should be used to extrapolate to the inhalation  RAC.
     This extrapolation method may introduce large uncertainties in the estimate of
     noncancer effects from inhalation  of these substances.  As discussed in U.S. EPA
     guidance for derivation of RfCs (U.S. EPA 1994J), the ability to perform quantitative
     route-to-route extrapolations is critically dependent on the availability of chemical-
     specific data on both the capabilities of the chemical to reach the target site for toxiciry
     and the nature of the toxic effect.  In cases where these data are not available, the use
     of default assumptions to perform  the route-to-route extrapolation results  in increased
     uncertainty associated with the derived RAC.  The magnitude of the uncertainty will be
     chemical-specific, and determined by the level of understanding provided by the
     supporting database as to the response of the human body to exposure to  the chemical.
          There may be several explanations for differences in toxicity when the route of
     administration differs, but the primary reason  is likely to  be related to the
     pharmacokinetics (i.e., absorption, distribution,  metabolism, and excretion) of the
     chemical.  Different routes of exposure may influence the factors that affect absorption
     at the portal of entry, such as the chemical's physicochemical properties (e.g.,
     dissociation state, solubility, or reactivity), the nature of the exposure (e.g.,
     concentration, duration, or regimen), or the physiologic parameters of the exposed
     tissues (e.g., metabolic capabilities, cell types, orpH).  Similarly, factors that affect the
     distribution of the chemical to the  various tissues in the body (e.g., solubility, chemical
     reactivity), the metabolism of the chemical (e.g., metabolic activation vs.  metabolic
     detoxification, metabolic capabilities of exposed  tissues), and the excretion of the
     chemical from the body (e.g., rate of clearance, site of excretion) all may be
     significantly affected by the route of exposure.  Thus, different routes of exposure  may
     have a strong impact on the delivered dose of the chemical at the target site of toxicity.
          For example, the portal of entry of the chemical may be exposed to  relatively high
     concentrations of the chemical. If the chemical  acts directly on  the local tissue  (e.g.,
     stomach or respiratory tract), or if the local tissue can metabolize the chemical to an
     active form, and if that tissue is susceptible to the effect of the chemical or its
     metabolites, lesions may arise preferentially at the site of  administration.  Chemicals
     administered orally (either by gavage, in feed, or in drinking water), pass directly from
     the  gastrointestinal (GI) tract via the portal system to the liver, and thus may be subject
     to "first pass" metabolism.  This in turn may either increase or decrease the toxic
     response,  depending upon whether the liver detoxifies or activates the chemical, and
Volnmp V
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\
V
 what tissue is susceptible to the toxic effects of the chemical.  A similar chain of events
 may occur for inhalation exposures, where metabolism of the inhaled chemical may
 occur at sites along the respiratory tract, thereby presenting the surrounding tissues.
 and, assuming systemic absorption, remote tissues with a metabolically-modified
 chemical.  Thus, one factor that must be considered in route-to-route extrapolations is
 the  metabolic capabilities of the tissues (in terms of both quantity and type of
 metabolites produced) at the different portals of  entry.
     If sufficient data are available, physiologically-based pharmacokinetic (PBPK)
 models are the preferred method for performing route-to-route extrapolations.
 However, PBPK models should be used in conjunction with mechanistic data to
 accurately extrapolate between different exposure scenarios. For example, the type of
 pharmacokinetic data that is relevant for chemicals whose mechanism of action involves
 toxicity at a site remote from the portal of entry  will be different from contact-site
 toxicants whose toxicity is based on high chemical reactivity to biological tissues.
     In those cases where sufficient data are not available to develop PBPK models,
 several methods for route-to-route  extrapolation can be employed that range in
 accuracy, and therefore,  inherent uncertainty, depending on the type  of data that is
 available. Dosimetric measures of bioavailability via different routes of exposure
 provide greater certainty in route-to-route  extrapolations, although the degree of
 uncertainty remains somewhat greater than that associated with full PBPK  modeling.
 However, simpler methods, such as the use of default absorption values for each
 exposure route appropriate to the type of chemical of concern are considered by U.S.
 EPA to be inadequate for quantitative route-to-route extrapolation (U.S. EPA 1994J).
     Based on U.S. EPA  (1990e) guidance,  route-to-route extrapolation is  used in
 developing RACs.  The compounds for which the procedure of route-to-route
 extrapolation is used to determine RACs are noted  in Tables ffl-l, m-4, and m-5.

 4.   Uncertainties Associated  with Substances  Without Toxicity Values
     Where  experimental data  on the toxicity of a given contaminant  are so limited that
 any useful toxicity value could not  be obtained, potential cancer risks and non-cancer
 health effects posed by the chemical through the  applicable exposure routes are not
 evaluated quantitatively.  However, many of the  chemicals with the greatest potential to
cause cancer and non-cancer toxic effects,  both on the basis of toxicity and of exposure
potential, have already been identified and studied.   For example, the National
Toxicology Program has studied the carcinogenic potential of approximately 450
chemicals to date and published the results in peer-reviewed, publicly available reports
(Huff 1996).  Other investigators have studied the carcinogenic potential  of about 800
           Volume V
                                                   TTT  1
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      additional chemicals (Gold et al.  1995).  Non-cancer toxic effects of a much larger
      number of chemicals have been investigated. Information on these effects are published
      in a number of publicly available data bases. Thus, the degree of underestimation of
      risks based  upon not evaluating the toxicities of chemicals with inadequate testing
      results, although not quantifiable, is expected to be relatively low.

      5.    Uncertainties Associated with Endocrine Disrupters
           An environmental endocrine disrupter may be defined as an exogenous agent  that
      interferes with the synthesis, secretion, transport,  binding, action, or elimination of
      natural hormones in the body.  These hormones are responsible for the .maintenance of
      homeostasis, reproduction, development, and behavior.
           The term "endocrine disruptors" (sometimes referred to as "environmental
      hormones") applies to any number of a broad class of chemical compounds with the
      ability to perturb or interfere with the finely-tuned endocrine system that is fundamental
      to normal function and homeostasis in cells, tissues and organisms at a variety of levels
      of biological organization.  Examples of chemicals suspected of being endocrine
      disruptors are the pesticides atrazine, DDT,  endosulfan, chlordane, heptachlor, 2,4,5-T,
      and 2,4-D.  Other chemicals that are potential endocrine distruptors are PCBs and
      dioxins/furans (The potential for noncancer health effects of  dioxins is discussed in
      Section B.I)
          The current concern about endocrine disruptors stems from a body of diverse
     historical information and more recent findings which have been integrated into  a
     working hypothesis.  The central theme of the hypothesis is that exposure to exogenous
     hormone-mimetic agents that interfere with the production, release, transport,
     metabolism, receptor binding, action or elimination of natural blood borne hormones
     and ligands can potentially lead to adverse health effects, particularly  effects on
     reproduction function.
          The data  that have contributed  to this working hypothesis stem from  a number of
     different disciplines.  These  include wildlife  reproduction  (feminization of birds,
     alligators, and certain terrestrial mammals); wildlife population ecology  (population
     declines);  human reproductive physiology (decreased sperm count in males in
     industrialized nations); epidemiology (observed increases in breast cancer in
     industrialized nations); molecular biology (receptor-mediated  mode of action data); and
     endocrinology  (increased understanding of mechanisms of hormone,regulation and
     impacts of perturbations).  These findings serve as a basis for further experimentation to
     determine whether the fundamental hypothesis is correct, and, if so, to what extent.
Volume V
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          The broad definition of chemicals which could qualify as endocrine disrupters is
     particularly problematic for the process of risk assessment.  These problems include the
     following:  1) reliance on limited, and in some cases conflicting, empirical data to
     support the designation of specific chemicals as endocrine disrupters: 2) lack of a clear
     structure-activity relationship among the diverse group of chemicals considered to be
     endocrine disrupters; 3) lack of unifying dose-response relationships among the diverse
     group of chemicals; and 4) existence of multiple modes of action for chemicals
     currently considered to be endocrine disrupters.
          Given the current limited state-of-the-science, it is premature to  attempt to evaluate
     the potential risks from human exposure to chemicals from the standpoint of endocrine
     disruption.  Therefore, the U.S. EPA  has not yet developed a methodology for the
     quantitative assessment of risks due to exposures to potential endocrine disrupters.
     However, the agency and other federal health regulatory and research agencies are
     sponsoring significant amounts of research to better understand the phenomenon of
     endocrine disruption so that it can be addressed  in future risk assessments.
Volume V
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TABLE lfl-1
Summary of Inhalation and Oral Toxicitv Values
Substance
Inhalation
RAC
Gig/m3)
Slope Factor
(mg/kg-day)'1
Oral
RfD
(mg/kg-day)
Slope Factor
(mg/kg-day)"1
PICs and Residual Organic Compounds (174)
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrolein
Acrylonitrile
Anthracene
Benzaldehyde
Benzene
Benzoic acid
Benzol a (anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Benzo(e)pyrene
Benzo(g , h , i)pery lene
Benzo(j )fl uoranthene
Benzo(k)fluoranthene
Benzotrichloride
Benzyl chloride
Biphenyl
Bis(2-chloroethoxy) methane
Bis(2-chloroethyl)ether
Bis(2-chloroisopropyl)ether
Bis(2-ethylhexyl)phthalate
Bromochloromethane
BromodichJoromethane
Bromoethene
Bromoform
Bromomethane
Bromodiphenylether, p-
Buladiene, 1,3-
53*
NL
2.3
88*
88*
0.005
0.5
260*
88*
1.5'
3,500*
NA
NA
NA
NL
NA
NL
NA
NA
NA
448
NA
NA
35'
18'
NA
18'
0.75
18'
1.3
NA
NA
NA
NL
7.7 x 10-3
NA
NA
NA
2.4 x 10-'
NA
NA
2.9 x 10-'
NA
NA
NA
NA
NL
NA
NL
NA
NA
NA
NA
NA
1.1
NA
NA
NA
NA
1.1 x 10-'
3.9 x 10-3
NA
NA
1.8
6.0 x 10 :
NL
NL
1.0 x ID'1
l.Ox 10-'
NA
i.ox 10-'
3.0 x 10-'
l.Ox 10-'
NA
4.0
NA
NA
NA
NL
NA
NL
NA
NA
NA
5.0 x 10':
NA
NA
4.0 x 10 2
2.0 x 10-:
NA
2.0 x 10:
NA
2.0 x 10 2
1.4x 10;3
NA
NA
NA
NL
NA
NA
NA
NA
5.4 x 10-'
NA
NA
2.9 x 10':
NA
7.3 x 10-'
7.3
7.3 x 10"'
NL
NA
NL
7.3 x 10:
13
1.7 x ID'1
NA
NA
1.1
NA
1.4x 10 2'
NA
6.2 x 10 =
NA
7.9 x 10°
NA
NA
NA
Volume V
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TABLE m-1 (continued)
Summary of Inhalation and Oral Toxicitv Values
Substance
Butanone, 2- (MEK)
Butylbenzylphthalate
Carbon disulfide
Carbon tetrachloride
Chlordane
Chloro-3-methylphenol, 4-
Chloroacetophenone, 2-
ChJoroaniline, p-
ChJorobeazene
Chlorobenzilate
Chloroethane
Chloroform
Chloromethane
Chloronaphthalene, beta
ChJorophenol, 2-
Chlorodiphenyl ether, 4-
Chloropropane, 2-
Chrysene
Cresol, m-
Cresol, o-
Cresol, p-
Crotonaldehyde
Cumene
D, 2,4-
DDE, 4,4'-
Dibenz(a,h)anthracene
Dibenz(a,h)fluoranthene
Dibromo-3-chIoropropane, 1,2-
DibromochJorornethane
Dichloro-2-buteneb, cis-1,4-
Dichloro-2-buteneb, trans- 1,4-
Dichlorobenzene, 1,2-
Dichlorobenzene, 1,3-
Dichlorobenzene, 1,4-
Inhalation
RAC
Gig/m3)
250
180*
2.5
0.5"
0.053*
NL
0.0075
3.5«
5.0
18'
2,500
8.8«
NA
70«
4.4'
NL
25
NA
441
441
4.4*
NA
2.3
8.8'
NA
NA
NL
0.05
18«
NA
NA
50
NA
200
Slope Factor
(mg/kg-day)'1
NA
NA
NA
5.3 x 10-=
1.3
NL
NA
NA
NA
2.7 x 10-'
NA
8.1 x 10-2
6.3 x 10-3
NA
. NA
NL
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NL
2.4 x 10-3
NA
9.3
9.3
NA
NA
NA
Oral
RfD
(mg/kg-day)
6x 10-'
2.0 x ID'1
1.0 x 10"'
7.0 x 10-1
6.0 x 10s
NL
NA
4.0 x 10°
2.0 x 10':
2.0 x 10':
NA
l.Ox 10 :
NA
8.0 x 10-2
5.0 x lO'3
NL
NA
NA
5.0 x 10"
5.0 x 10'2
5.0 x lO'3
NA
4 x 10-2
l.Ox 10 :
NA
NA
NL
NA
2.0 x lO'2
NA
NA
9 x ia:
NA
NA
Slope Factor
(mg/kg-day)"1
NA
NA
NA
1.3 x 10'
1.3
NL
NA
NA
NA
2.7 x 10"'
NA
6.1 x 10°
1.3x 10':
NA
' NA
NL
NA
7.3 x 10°
NA
NA
NA
1.9
NA
NA
3.4 x ID'1
7.3
NL
1.4
8.4 x W~
NA
NA
NA
NA
2.4 x 10-:
Volume V
-------
TABLE ffl-1 (continued)
Summary of Inhalation and Oral Toxicity Values
Substance
Dichlorobenzidine, 3,3'-
Dichlorobiphenyl
Dichlorodi fluoromethane
Dichloroethane, 1,1-
Dichloroethane, 1,2-
Dichloroethene, 1,1-
Dichloroethene, trans- 1,2-
Dichloro fluoromethane
Dichlorophenol, 2,4-
Dichloropropane, 1,2-
Dichloropropeneb, cis-1,3-
Dichloropropeneb, trans-1.3-
Diethylphthalate
Dimethoxybenzidine, 3,3'-
Dimethylphenol, 2,4-
Dimethylphthalate
Di-n-butylphthalate
Di-n-octylphthalate
Dinitrotoluene, 2,6-
Dinitro-2-methylphenol, 4.6-
Dinitrobenzene, 1,2-
Dinitrobenzene, 1,3-
Dinitrobenzene, 1,4-
Dinitrophenol, 2,4-
Dinitrotoluene, 2,4-
Dioxane, 1,4-
Ethyl methacrylate
Ethylbenzene
Ethylene dibromide
Ethylene oxide
Ethylene thiourea
Fluoranthene
Fluorene
Formaldehyde
Inhalation
RAC
G*g/m>)
NA
NA
50
130
NA
7.9'
18*
NL
2.6'
1.0
5.0
5.0
700*
NA
18*
NA
88'
18'
0.88'
NL
0.35'
0.088'
0.35'
1.8'
1.8'
NA
79,
250
0.05
NA
0.07*
35*
35«
ISC'
Slope Factor
(mg/kg-dayV1
NA
NA
NA
NA
9.1 x 10-2
1.2
NA
NL
NA
NA
1.3 x 10-'
1.3 x 10-'
NA
NA
NA
NA
NA
NA
NA
NL
NA
NA
NA
NA
NA
NA
NA
NA
7.6 x 10-'
3.5 x 10-'
NA
NA
NA
4.5 x ID"2
Oral
RfD
(mg/kg-day)
NA
NA
2 x 10-'
1.0 x lO'1
NA
9.0 x 10 3
2.0 x 10":
NL
3.0 x 10'3
NA
3.0 x 10"4
3.0 x 10"1
8.0 x 10-'
NA
2.0 x 10:
NA
l.Ox 10"'
2.0 x 10':
l.Ox 10-3
NL
4.0 x 10J
l.Ox 10-*
4.0 x 10-4
2.0 x 10 3
2.0 x 10°
NA
9.0 x 102
l.Ox 10-'
NA
NA
8.0 x ID'3
4.0 x 10 :
4.0 x lO'2
2.0 x 10-'
Slope Factor
(mg/kg-day)"1
4.5 x 10 :
7.7-'
NA
NA
9.1 x 10 :
6 x 10 '
NA
NL
NA
6.8 x 10:
1.8x 10-'
1.8x 10-'
NA
1.4x 10':
NA
NA
NA
NA
6.8 x lO'1
NL
NA
NA
NA
NA
6.8 x 10-'
1.1 x 10'2
NA
NA
85
1.0
1.1 x 10-'
NA
NA
NA
Volume V
-------
TABLE m-1 (continued)
Summary of Inhalation and Oral Toxicity Values
Substance
Furfural
Heptachlor
Heptachlorobiphenyl
Hexachlorobenzene
Hexachlorobiphenyl
Hexachlorobutadiene
Hexachlorocyclohexane, alpba-
Hexachlorocyclohexane, beta-
Hexachlorocyclohexane, gamma-
(Lindane)
Hexachlorocyclopentadiene
HexacbJoroethane
Hexachlorophene
Hexane. n-
Hexanone, 2-
Hexanone, 3-
Indeno( 1 ,2,3-cd)pyrene
Isophorone
Maleic hydrazide
Methoxychlor
Methylene bromide
Methylene chloride
Methylnaphthalene, 2-
Methyl-2-pentanone, 4- (MIBK)
Methyl-tert-butyl ether
Monochlorobiphenyl
Naphthalene
Nitroaniline, 2-
Nitroaniline, 3-
Nitroaniline, 4-
Nitrobenzene
Nitrophenol, 2-
Nitrophenol, 4-
N-Nitroso-di-n-butylamine
Inhalation
RAC
G*g/mJ)
13
0.44'
NA
0.7*
NA
0.18"
NA
NA
0.26'
0.018
0.88'
0.26'
50
NL
NL
NA
180'
440'
4.4s
8.8'
750
NL
20
750 .
NA
35
0.05
NL
NL
0.5
NL
NL
NA
Slope Factor
(mg/kg-day)'1
NA
4.5
NA
1.6
NA
7.8 x 10-:
6.3
1.8
NA
NA
1.4x 10"2
NA
NA
NL
NL
NA
NA
NA
NA
NA
1.6 x 10'3"
NL
NA
NA
NA
NA
NA
NL
NL
NA
NL
NL
5.4
Oral
RfD
(mg/kg-day)
3.0 x 10-'
5.0 x 10J
NA
8.0 x 10J
NA
2.0 x 10-* .'
NA
NA
3.0 x 10-1
7.0 x ID'3
l.Ox lO'3
3.0 x 10-1
6.0 x ID'2
NL
NL
NA
2.0 x 10-'
5.0 x ID'1
5.0 x lO'3
l.Ox lO'2
6.0 x lO'2
NL
8 x 10--
NA
NA
4x 10-2
NA
NL
NL
5.0 x 10-4
NL
NL
NA
Slope Factor
(mg/kg-day)"1
NA
4.5
l.T
1.6
7.7C
7.8 x 10:
6.3
1.8
1.3
NA
1.4x 10-:
NA
NA
NL
NL
7.3 x 10-'
9.5 x W
NA
NA
NA
7.5 x JO'3
NL
NA
NA
7.7C
NA
NA
NL
NL
NA
NL
NL
5.4
Volume V
-------
TABLE ffl-1 (continued)
Summary of Inhalation and Oral Toxicity Values
Substance
N-Nitroso-di-n-propylamine
N-Nitrosodiphenylamine
Nonachlorobiphenyl
Octachlorobiphenyl
Pentachlorobenzene
Pentachlorobiphenyl
Pentachloronitrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Phosgene
Propionaldehyde
Pyrene
Quinoline
Quinone
Safrole
Styrene
Tetrachlorobenzcne, 1,2,4,5-
TetrachJorobiphenyl
Tetrachloroethane, 1.1,1,2-
Tetrachloroethane, 1,1,2,2-
Tetrachioroethene
Tetrachlorophenol, 2,3,4,6-
Toluene
Toluidine, o-
Toiuidine, p-
Trichloro-l,2,2-TFE, 1,1,2-
Trichlorobenzene, 1,2,4-
Trichlorobiphenyl
Trichloroethane, 1,1,1-
Trichloroethane, 1,1,2-
Trichloroethene
Trichlorofluoromethane
Trichlorophenol, 2,4,5-
Inhalation
RAC
(pgln?)
NA
NA
NA
NA
NA
NA
2.6s
26«
NA
530«
NL
NL
26'
NA
NL
NL
250
0.26'
NA
26'
NA
8.8«
26»
100
NA
NA
7.500
50
NA
250f
3.5'
NA
180
88«
Slope Factor
(mg/kg-day)*1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NL
NL
NA
NA
NL
NL
NA
NA
NA
2.6 x 10-:
2.0 x 10-'
2.0 x 103f
NA
NA
NA
NA
NA
NA
NA
NA
5.7 x 10-;
6.0 x 10'3f
NA
NA
Oral
RfD
(mg/kg-day)
NA
NA
NA
NA
8.0 x 10"
NA
3.0 x lO'3
3.0 x 10 :
NA
6.0 x ID'1
NL
NL
3.0 x 10 :
NA
NL
NL
2.0 x 10-'
3.0 x 10J
NA
3.0 x 10:
NA
l.Ox 10 :
3.0 x 10-2
2.0 x 10-'
NA
NA
3.0 x 10'
l.Ox 10-:
NA
NA
4.0x,10'3
NA
3 x 10"'
l.Ox 10-'
Slope Factor
(mg/kg-day)"'
7.0
4.9 x 10'"'
7.7C
7.7'
NA
i.r
2.6 x lO'1
1.2x 10-'
NA
NA
NL
NL
NA
12
NL
NL
NA
NA
7.7'
2.6 x 10":
2.0 x 10-'
5.2 x 10-*
NA
NA
2.4 x 10-'
1.9x 10-'
NA
NA
l.T
NA
5.7 x 10 :
1 . 1 x 10"2'
NA
NA
Vr.li
-------
TABLE m-1 (continued)
Summary of Inhalation and Oral Toxicity Values
Substance
Trichlorophenol, 2,4,6-
Trichloropropane, 1,2,3-
Vinyl acetate
Vinyl chloride
Xylene, m-
Xylene, o-
Xylene, p-
Inhalation
RAC
(Ag/m3)
NA
5.3'
50
NA
1,800*
1,800*
NA
Slope Factor
(mg/kg-day)"1
l.Ox 10-:
NA
NA
3.0 x 10-'
NA
NA
NA
Oral
RfD
(mg/kg-day)
NA
6.0 x 10-?
1.0
NA
2.0
2.0
NA
Slope Factor
(mg/kg-day) '
1.1 x 10 :
7.0
NA
1.9
NA
NA
NA
Dioxin and Furan Congeners (17)
2,3,7, 8-TCDD
1, 2,3,7, 8-PeCDD
1,2,3,4,7,8-HxCDD

1,2,3,6,7,8-HxCDD
1,2,3,7,8,9-HxCDD

1,2,3,4,6,7,8-HpCDD

OCDD
2,3,7,8-TCDF
1, 2,3,7, 8-PeCDF
2,3,4,7, 8-PeCDF
1,2,3,4,7,8-HxCDF

1,2,3,6,7,8-HxCDF

2,3,4,6, 7, 8-HxCDF

1,2,3,7,8.9-HxCDF

1,2,3.4,6,7,8-HpCDF

1.2,3,4,7.8,9-HpCDF
OCDF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1.5 x 10s
7.5 x 104
1.5 x 104
1.5 x 104
1.5 x 104
1.5 x 103
1.5 x l(f
1.5 x 104
7.5 x 103
7.5 x 104
1.5 x 104
1.5 x 104
1.5 x 104
1.5 x 104
1.5 x 103
1.5 x 103
1.5 x 10=
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1.5 x 105
7.5 x 104
1.5 x 104
1.5 x 10"
1.5 x 10"
1.5 x 103
1.5 x 102
1.5 x 10"
7.5 x 103
7.5 x 104
1.5 x 10"
1.5 x 10"
1.5 x 10"
1.5 x 10"
1.5x 103
1.5 x 103
1.5 x 10=
Metals (17)
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
NA
0.35'
0.26*
0.13
4.4'
0.44'
4.4s
NA
NA
50
NA
8.4
6.1
41
NA
4.0 x 10-4
3.0 x 10"1
7.0 x 10':
5.0>x 10'3
5.0 x 10^
5.0 x 10'3
NA
NA
1.75"
NA
4.3
NA
NA
Volume V
-------
TABLE m-1 (continued)
Summary of Inhalation and Oral Toxicity Values
Substance
Chromium (trivalent)
Copper
Lead
Mercury
Methylmercury'
Nickel
Selenium
Silver
Thallium'
Zinc
Inhalation
RAC
Gig/mJ)
880*
NA
NA
0.075
0.075*
18*
4.4'
4.4*
0.061*
260*
Slope Factor
(mg/kg-day)"1
NA
NA
NA
NA
NA
0.84
NA
NA
NA
NA
Oral
RfD
(mg/kg-day)
1.0
NA
NA
3.0 x 10-*
3.0 x 10-1
2.0 x 10": .
5.0 x 103
5.0 x ID'3
7.0 x lO'5
3.0 x lO'1
Slope Factor
(mg/kg-da>V'
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Acid Gases and Particulate Matter (5)
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Particulate matter
Respirable particulates
1.8
NL
NL
NL
NL
NA
NL
NL
NL
NL
NA
NL
NL
NL
NL
NA
NL
NL
NL
NL
Notes:
All values from IRIS or HEAST unless otherwise noted cDD - chlorodibenzo-p-dioxin
> - On recommendation from EPA, ECAO (provisional) cDF - chlorodibenzofuran
b - Value for mixed isomers RfD . reference dose
c - Value for PCBs, in general RAC . reference air concentration, esumaied to be
d - Calculated from unit risk 25% of the RfC
e - Value for thallic oxide (highest potency salt) ypj . trifluoroethane
f - Superfiind Health Risk Technical Support Center per MffiK - methyl isobutyl ketone
HEAST. MEK - methyl ethyl ketone
g - RAC estimated baud on route-to-route extrapolation NA . dita not av.ilable for EPA to make a
from RfD. quantitative assessment
NL - compound not listed in IRIS or HEAST
h - In this assessment, concentrations of these substances are compared to NAAQS: 100 ng/nf for nitrogen dioxide, 80 ^g/m'
for sulfur dioxide; and 50 /ig/m5 for PM,0.
i - Although methylmercury is referred to as an 'organic* form of mercury, it is classified in this table, and in this assessment,
with the metals.
The number of substances in each group is indicated in parentheses
Volume V
-------
TABLE ffl-2
Toxicity Equivalence Factors (TEFs) for Dioxins and Furans*
Congener
2,3,7,8-TCDD
1,2,3,7.8-PeCDD
1, 2,3,4,7, 8-HxCDD
1,2,3,6,7, 8-HxCDD
1,2,3,7, 8, 9-HxCDD
1,2,3,4,6.7.8-HpCDD

OCDD
2,3,7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4.7,8-PeCDF
1,2,3,4,7,8-HxCDF
1,2,3,6,7, 8-HxCDF
1,2,3,7,8,9-HxCDF
2,3,4.6.7,8-HxCDF

1,2,3,4,6,7,8-HpCDF
1,2,3,4,7,8.9-HpCDF

OCDF
TEF
1
0.5
0.1
0.01
0.001
0.1
0.05
0.5
0.1
0.01
0.001
Notes
a - U.S EPA 1994b
CDD - chlorodibenzo-p-dioxin
CDF - chlorodibenzofuran
Volume V
-------
TABLE IH-3
Relative Potency of Carcinogenic
Polycydic Aromatic Hydrocarbons (PAHs)
Polycyclic Aromatic Hydrocarbon
Benzo[a]pyrene
Benzo[a]anthracene
Benzo[b]fluoranthene
Benzo[k]fluoranthene
Chrysene
Dibeozo[a,h]anthracene
Lndenofl ,2,3-cd]pyrene
Relative Potency
1
0.1
0.1
0.1
0.01
1
0.1
Reference: U.S. EPA 1993c
Volume V
-------
TABLE m-4
Summary of Inhalation Toxicity Values for Substances of Potential Concern
(Fugitive Vapor Emissions)
Substance of Potential Concern
Inhalation
Slope Factor
(mg/kg-day)"1
Organic Compounds
Acetone
Acetonitrile
Acetophenone
Acetylaminofluorene, 2-
Acrylonitrile
Alcohols
Aliphatic hydrocarbons
Aniline
Benzene
Benzenedicarboxylic acid, 1,2-
Benzidine
Benzoquinone, p-
Beozo(a)pyrene
Butanol
Bulanone, 2-
Butyl acetate
Calcium chromate
Carbon
Carbon disulfide
Carbon tetrachloride
Chlorobenzene
Chloroform
Chlorinated paraffin, oil, wax
Chrysene
Creosote (coal tar)
Cresol
Crotonaldehyde
Cumene
Cyclohexane
Cyclohexanone
NA
NA
NA
NL
0.24
NL
NL
NA
0.029
NA
230
NL
NA
NA
NA
NA
NL
NL
NA
0.053
NA
0.081
NL
NA
NL
NA
NA
NA
NL
NA
RAC
Oig/m3)

88a
13
88'
NL-
0.50
NL
NL
0.25
NA
880"
2.6'
NL
NA
88
250
44'
NL
NL
2.5
0.50-
5.0
8.8'
NL
NA
NL
4.4'
NA
2.3
NL
'" 4400"
Volume V
-------
TABLE HI-4 (continued)
Summary of Inhalation Toxicity Values for Substances of Potential Concern
(Fugitive Vapor Emissions)
Substance of Potential Concern
Dibenz(a,h)anthracene
Dibromoethane, 1,2-
DichJorobenzene
Dichlorodifluoroethane
Dichlorodifluoromethane
Dichloroethane, 1,1-
Dichloroethene
Diethyl stilbestrol
Diethylphthalate
Dimethyl sulfate
Dimethylamine
Dimethylbenzidine, 3,3'-
Dimethylhydrazine
Dimethylphenol, 2,6-
Dimethylphthaiate
Dinitrotoluene
Dioxane, 1,4-
Epichlorohydrin
Ethanol
Ethoxyethanol, 2-
Ethyl acrylatc
Ethyl benzene
Fluoranthene
Formaldehyde
Formic acid
Furfural
Heptane
Hydrazine
Indenod ,2,3-cd)pyrene
Isobutanol
Isopropanoi
Inhalation
Slope Factor
(mg/kg-day)"1
NA
0.76
NA
NL
NA
0.091
1.2
490
NA
NA
NL
NA
NA
NA
NA
NA
NA
0.0042
NL
NA
NA
NA
NA
0.045
NA
NA
NL
17
0.73
NA
NL
RAC
Gig/m3)
NA
0.05
50
NL
50
120
7.9"
NA
700"
NA
NL
NA
NA
0.53"
NA
0.88"
NA
1.8-
NL
50"
NA
250
35"
180"
1,800-
13
NL
NA
NA
250"
'NL
Volume V
-------
TABLE m-4 (continued)
Summary of Inhalation Toxicity Values for Substances of Potential Concern
(Fugitive Vapor Emissions)
Substance of Potential Concern
Isosafrole
Maleic anhydride
Methanol
Methyl methacrylate
Methylbutadiene, 1-
Methylcholanthrenc, 3-
Methyl isobutyl ketone
Naphthalene
Naphthylamine, 1-
Naphthylamine, 2-
Nitrobenzene
Nitrophenol, 4-
Nitropropane, 2-
N-nitrosodiethanolamine
N-nitrosodiethylamine
N-nitrosodi-n-butylamine
N-nitrosopyrolidine
Phenol
Phthalic anhydride
Picoline, 2-
Pyridine
Resorcinol
Tetrachlorobenzene, 1,2,4,5-
Tetrachloroethane, 1,1,1,2-
Tetrachloroethene
Tetrahydofuran
Toluene
Toluene diisocyanate
Toluenediamine
Trichloro-l,2,2,-trifluoroethane, 1,1,2-
Trichlorobenzene
Inhalation
Slope Factor
(mg/kg-dayV1
NL
NA
NA
NA
NL
NL
NA
NA
NL
NL
NA
NL
9.4
NA
150
5.4
2.1
NA
NA
NA
' NA
NL
NA
0.20
0.052
NL
NA
NL
NA
NA
NA
RAC
Oig/m3)
NL
88"
440"
70*
NL
NL
20
35
NL
NL
0.50
NL
5.0
NA
NA
NA
NA
530*
30
NL
0.88"
NL
0.26'
26'
8.8'
NL
100
NL
175
7,500
50
Volume V
-------
                                         TABLE HI-4 (continued)
                Summary of Inhaladon Toxicity Values for Substances of Potential Concern
                                        (Fugitive Vapor Emissions)
              Substance of Potential Concern
 Inhalation
Slope Factor
(mg/kg-dayy1
 RAC
(fig/m3)
           Trichloroethane, 1,1,1-
     NA
 250
           Trichloroethene
   0.011
 NA
           Trichlorofluorometbane
     NA
  175
           Xylene
     NA
 1,800"
           Notes:
           Values derived from IRIS and HEAST
           RAC - reference air concentration, estimated to be 25 % of the RfC.
           NA - data not available for EPA to make a quantitative assessment
           NL - compound not listed in IRIS or HEAST
           a  - RAC estimated based on route-to-route extrapolation from RfD.
Volume V
-------
TABLE ffl-5
Summary of Inhalation and Oral Toxicity Values for Metals of Potential Concern
(Fugitive Ash Emissions)
Metal/Inorganic
Compound
Arsenic
Barium
Cadmium
Lead
Nickel
Selenium
Silver
Cyanide
Inhalation
RAC
(Aig/m3)
0.26"
0.13
0.44'
NA
18"
4.4'
4.41
18«
Slope Factor
(mg/kg-day)'1
50
NA
6.1
NA
0.84
NA
NA
NA
Oral
RfD
(mg-kg-day)
3.0 x icr1
7.0 x 10-=
5.0 x 104
NA
2.0 x 10-=
5.0 x 10"J
5.0 x 10-3
2.0 x 10':
Slope Factor
(mg/kg-day)"1
1.75"
NA
NA
NA
NA
NA
NA
NA
Notes-
All values from IRIS or HEAST unless otherwise noted
a - RAC estimated based on route-to-route extrapolation from RfD.
b - Calculated from unit risk
Volume V
-------
TABLE III-6
Key Assumptions Tor Chapter III
(Toxicity Assessment)
Assumption
The following assumptions are implied in using EPA
toxicity values in the assessment:
The chemical toxicity values in IRIS and HEAST
are accurate
A "no-threshold" assumption has been applied for
exposure to carcinogens
The SF is based on the upper 95% confidence
limit based on the linearized multistage model
A "threshold" assumption has been applied for
exposure to chemicals with non-carcinogenic
affects
The RfD is related to the NOAEL or LOAEL by
uncertainty factors
Oral values apply for dermal exposures
RACs are developed from oral RfDs when RfCs are not
available
Nickel is evaluated for both carcinogenic and
noncarcinogenic effects
Dioxin-like compounds are assigned cancer slope factors
based on the TEF scheme
The cancer slope factors of PAHs are assigned based on a
relative potency scheme
Basis
Toxicity values presented in IRIS and HEAST reflect
EPA's conservative assessment of the available data
and include safety factors as appropriate.
It is conservative to assume that oral data apply
when there is a lack of data for the inhalation route.
A conservative assumption because there is no direct
evidence that the forms of nickel expected to be
emitted from hazardous waste combustion units are
carcinogenic. IARC and U.S. EPA, however, both
recognize that certain forms of nickel could be
carcinogenic by the inhalation route.
The internationally accepted approach is used in this
assessment.
EPA (I993c) interim guidance based on results in a
group of carcinogenicity studies in animals.
Magnitude
of Effect
low to
medium
low
low
low
low
Direction of
Effect
overestimate
overestimate 1
overestimate
overestimate

Volume V
111-32
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TABLE II 1-6 (continued)
Key Assumptions for Chapter III
(Toxicity Assessment)
Assumption
Toxicity values are not derived if insufficient toxicity data
are available
NAAQS are protective of human health
Basis
Adequate data from well designed and conducted
studies are required to derive a toxicity value.
NAAQS have been developed by EPA using
conservative assumptions to ensure they would be
protective of human health.
Magnitude
of Effect
unknown
low
Direction of
Effect
underestimate
overestimate
Notes-
low = less than a factor of two
medium = a factor of two lo ten
high = greater than a factor of ten
Volume V
                                                                 III 33
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              IV.  SELECTION OF SURROGATE CHEMICALS
 A.  Selection of Chemicals in Stack Emissions to Evaluate in the Risk Assessment
     As identified in the preceding chapters, almost 200 organic compounds are identified
 that could potentially be released from the incinerator stack.  Human health risks associated
 with direct inhalation of each of these compounds are quantitatively evaluated in the HHRA.
 In order to focus the assessment of risks from indirect pathways of exposure, a subset of the
 organic compounds listed in Table 1-1 is selected that are predicted to contribute most of the
 risks.  This subset of compounds, referred to as the "surrogate organic chemicals", is the
 subject of further quantitative evaluation.
     In assessing the risks associated with indirect exposure to organic compounds emitted
 from the stack, the selection of surrogate  chemicals focuses on the organic residues and PICs
 that are highly toxic and have the  greatest potential to accumulate in environmental media.
 Surrogate organic chemicals are selected based on the following factors:

     Emission Rate - as reflected by data collected during trial bums and performance tests
     at the WTI facility, as estimated earlier;

     Toxicity  - considering both carcinogenic and noncarcinogenic effects; and

     Bioaccumulation Potential - based on the octanol/water partition coefficient, K^, a
     measure of a chemical's likelihood to bioaccumulate.

     The surrogate chemicals selection process consists of two steps and is in general
agreement with the most recent U.S. EPA guidance for conducting risk assessments at RCRA
hazardous waste  combustion units  (U.S. EPA 1994a), with the following deviation.  K^ is
used in the selection process instead of log K^  to be consistent with the bioaccumulation
equations in the fate and transport  modeling.  The use of K^, will lead to the selection of
chemicals that  are the most likely to bioaccumulate, and therefore, present the greatest
significance in the indirect risk assessment.  Chemicals that are selected by this approach
may be further evaluated for their  persistence and bioaccumulation potential in environmental
media and the  food chain.  The factors to  be evaluated would  include the potential for
Volume V
                                        T\T 1
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 biodegradation, absorption, metabolism, and excretion.  The following steps outline the
 methodology used in the surrogate chemical selection process.

     Step 1:   Selection of Surrogates on the Basis of Quantity, Carcinogenic Potency.
               and Bioaccumulation Potential

          In Step  1, 17 dioxin and furan congeners and 174 organic residues and PICs are
     ranked on the basis of estimated quantity emitted, carcinogenic potency, and
     bioaccumulation potential, as determined by the following equation:

                                 QCB = (ER)(SF)(KOW)                           (IV-1)

     where:
          QCB      =   quantity/carcinogenic potency/bioaccumulation potential score
          ER       =   estimated emission rate
          SF        =   slope factor (oral or inhalation, whichever is higher [to be
                        conservative])
          K^       =   octanol-water partition coefficient, which is related to a  chemical's
                        bioaccumulation potential in milk, meat, and fish.

          Average emission rates  in the above equation for the dioxin and furan congeners
     and PICs are  estimated as described in Volume ffl.  Emission rates are not available for
     31 compounds; consequently, these compounds are not evaluated in this assessment.
          Chemical-specific values for the  octanol-water partition coefficient, K^, used in
     the above equation are obtained  from  the literature.  K^, values reported in the scientific
     literature often vary (sometimes  by more than an order of magnitude) from one source
     to another, depending on the  methodology used to derive  the value.  Therefore, the
     selection of K^ values used in calculating  QCB scores is  conducted using  the following
     sources.  For the dioxin and  furan congeners and chlorinated biphenyls, K^, values are
     obtained from the report, Estimating Exposure to Dioxin-Like Compounds  (U.S. EPA
     1994b).  For the PICs, the U.S. EPA document titled: Internal Report on  Summary  of
     Measured, Calculated and Recommended Log K^, Values (U.S. EPA 1995b)  is used as
     the primary source of K^ values.  The K^ values recommended in this document are
     used in the HHRA.  K^ values are not available in this source for 29 compounds, so
     other sources  are relied upon, including Howard (1993), the National Library of
     Medicine's Hazardous Substance Data Bank (HSDB), U.S. EPA (1990f), Verschueren
     (1983), and Montgomery and Welkom (1990). For chemicals that have multiple Kow

Volume V                               *-"• ~
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      values listed in these sources, the maximum value is conservatively applied in this
      assessment. It should be noted that a K^. value could not be found in the literature for
      dibenzo(a,h)fluoranthene.  This chemical, therefore, is not evaluated in this assessment.
      The log K^, values used in this assessment are presented in Appendix V-l.
          Slope factors, obtained from the U.S.  EPA Integrated Risk Information System
      (IRIS) and HEAST (U.S. EPA  1994d) data bases, are listed in Table m-1. Chemicals
      for which slope factors are not available from these sources are not considered in this
      step. Of the chemicals considered, slope factors are not available for 77 compounds
      (the absence of slope factors indicates that these compounds have not exhibited
      carcinogenic effects in toxicity studies or not enough data were available for U.S. EPA
      to derive cancer toxicity values).  These compounds may have noncarcinogenic effects
      and  are included in Step 2. A tabulation of the emission rates, slope factors,  and K^
      values used in estimating QCB scores is presented in Appendix V-2. (Appendix  V-2
      does not include the 31 compounds for which emission rates are not available.)
          The 65 PICs and 17 dioxins/furans for which slope factors were available are
      ranked on the basis of QCB score and 8 surrogate organic compounds (plus 17
      dioxin/furan congeners)  are selected for evaluation in the HHRA. As can be seen from
      Table IV-1, which shows the chemicals with the highest QCB scores, the dioxin and
      furan congeners account for approximately 95% of the total QCB score.   Additionally,
     the 17 dioxin and  furan congeners and 8 organic PICs that are retained by the screen
      incorporate approximately 99.8% of the total QCB score.  The cutoff criterion is
     selected to ensure all the dioxin and furan congeners are included.  It should be noted,
     however, that of the eight surrogate organic compounds selected, only one, bis(2-
     ethylhexyl)phthalate, was detected during the August 1994 PIC testing.
          In addition to the compounds selected on the basis of the  QCB score, two PCBs,
     tetrachlorobiphenyl and hexachlorobiphenyl, are included for quantitative evaluation in
     the HHRA to represent PCB compounds that have  high bioaccumulation  potential.

     Step 2:  Selection of Surrogates on the Basis of Quantity, Noncarcinogenic
              Toxicity, and Bioaccumulation Potential

          In Step 2, organic chemicals are ranked on the basis of quantity, noncarcinogenic
     toxicity, and bioaccumulation potential,  as determined using the following equation:

                                QNB = (ER)(Kow)/RfD          '                (TV-2)
Volume V
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     where:
          QNB     =    quantity/non-cancer toxicity/bioaccumulation potential score
          ER       =    emission rate
          KOT       =    octanol-water partition coefficient, which is related to a chemical's
                         bioaccumulation potential in milk, meat, and fish
          RfD      =    reference dose  (oral or inhalation, whichever is smaller to be
                         conservative).

          RfD values, obtained from IRIS and HEAST (U.S. EPA 1994d) data bases, are
     listed in Table EM and in Appendix V-2.  The 72 chemicals (this includes the 17
     dioxins/furans) for which RfD values are not available are not included in this step.
     Emission rates and K^ values are estimated using the methods described earlier.
          The results of Step 2 for the 87 chemicals  with RfD values are presented in Table
     IV-2. A cutoff of 99% of the total  QNB score is used, resulting in five chemicals being
     retained on the basis of emission rate, toxicity, and bioaccumulation potential.  With the
     exception  of bis(2-ethylhexyl)phthalate, none of the surrogate chemicals selected on the
     basis of QNB score were detected in the August 1994 PIC testing at the WTI facility.
          Carbon tetrachloride is also retained for evaluation in the HHRA since it is the
     next highest ranked compound (based on QNB score) that was actually detected in the
     August 1994 PIC testing. Table IV-3 contains a listing of all chemicals to be evaluated
     in the indirect risk assessment.

     In summary, 8 surrogate organic compounds and 17 dioxin/furan congeners are selected
for evaluation on the basis of QCB score.  Two PCBs (tetrachlorobiphenyl and
heptachlorobiphenyl) are selected on the basis of bioaccumulation potential.  Five chemicals
are selected on  the basis of QNB score [bis(2-ethylhexyl)phthalate appears on both the  QCB
and QNB lists].  In addition, carbon tetrachloride is added to the QNB list to provide another
chemical that was actually detected in PIC testing.  The list of surrogate organic compounds
evaluated in the HHRA is  shown in Table IV-3.  All  of the metals for which toxicity data are
available (see Table DI-1)  are included in Table  IV-3. Appendix V-2 provides a list of the
organic compounds (142 organic compounds and 17 dioxins/furans) considered  in the
assessment  for which emission rates or K^ values are available.  The emission rates, slope
factors, reference doses, and octanol-water coefficients used in  calculating the QCB and QNB
scores  are also presented in Appendix V-2.
                                                                 f'"*
     It should be noted that once a surrogate organic  chemical is selected, it is evaluated in
the HHRA  for both cancer and noncancer toxicity, regardless of the basis of its selection
(i.e., chemicals selected on the basis of carcinogenic potential are also evaluated for

Volume V                                ~*  •
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noncancer effects, if noncancer toxicity values arc available.  Similarly, chemicals selected
on the basis of noncancer toxicity are also evaluated for carcinogenic potential, if cancer
toxicity values are available).

B.  Partitioning of Emissions Between the Vapor and Particle Phases
     As discussed in Volume ffl, stack gas from the WTI incinerator contains substances
present in either the vapor phase  or as particles.  When the stack gas is emitted to the
atmosphere, vapor-phase substances will either remain in the vapor phase or adsorb onto
particles present in the gas stream.  The methodology for predicting  this partitioning is
described in Volume IE.  This methodology is applied to the dioxin/furan compounds,  the
surrogate  organic chemicals selected in the previous sections  of this chapter, and mercury.
     The  fraction of organic chemicals that adsorbs to particles is estimated using the
equations  in Volume HI and is presented in Table IV-4 for the dioxin and furan congeners,
mercury,  and the surrogate organic chemicals representing PIC and residual organic
compounds emissions from the stack (also see Appendix V-3).  The polycyclic aromatic
hydrocarbons dibenz(a,h)anthracene and indeno(l,2,3-cd)pyrene, which have very low  vapor
pressures  (i.e., less than 10'10 mm Hg), and all the metals, with the exception of mercury,
are assumed to be present entirely as particles.

C.  Selection of Chemicals to Evaluate in Fugitive Emissions Analysis
     Residents in the immediate vicinity of the WTI facility may be exposed to fugitive
emissions  of volatile organic compounds from the site. Fugitive chemicals  are primarily
volatile constituents present in the waste feed that are released during waste handling and
processing prior to incineration.   These volatile constituents are released from locations close
to ground elevation and are likely to have a more localized impact than chemicals emitted
from the stack.  Consequently, the surrogate selection procedure for  fugitive emissions  is
directed towards identifying chemicals present in the waste feed that  are of concern as a
result of direct inhalation exposures.
     Following the selection of the surrogate fugitive organic chemicals for analysis,
chemical-specific emission rates are estimated, based on the physical-chemical properties of
the surrogate chemicals.

     1.   Selection of Surrogate Chemicals  in Fugitive Vapor Emissions
          More than 300 organic  compounds are identified as being in  the pumpable feed at
     the facility, likely to be the most significant source of fugitive emissions from the  WTI
     facility.  To focus the risk assessment of fugitive organic vapor  emissions, a subset of
     these compounds, referred to as surrogate chemicals,  is developed.  The selection  of

Volume V                               r\r <
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      surrogate chemicals that significantly contribute to health risks associated with fugitive
      organic vapor emissions from the WTI facility is based on the quantity, volatility, and
      toxicity of the chemicals as follows:

          Quantity - quantity is accounted for by estimating the total moles of each chemical
          that are processed by WIT, based on the total pounds annually in the pumpable
          feeds at the facility and  the molecular weight of the chemicals;

          Volatility - volatility of each compound is accounted for by its vapor pressure,
          which reflects the equilibrium  of the chemical between the vapor and condensed
          (i.e., generally liquid) phases at a specific temperature (25°C assumed);  and

          Toxicity - toxicity is evaluated using cancer slope factors (SFs) and noncancer
          reference doses (RfDs) that have been compiled by U.S. EPA. When available.
          SFs and RfDs for the inhalation route  of exposure are used; however, for many
          chemicals only oral toxicity values are available, and these are conservatively
          applied.  Oral toxicity values are used to estimate inhalation toxicity for 28
          chemicals with non-cancer chronic toxicities.

          To facilitate the surrogate selection process, the original list of approximately 300
     chemicals identified in  the pumpable waste feed is condensed to a list of 96 chemicals
     that account for 90 percent of the total pumpable feed processed in a year, as  presented
     in Appendix V-4.  These 96 compounds are evaluated using the following methodology.

     Step 1:    Selection of  Chemicals Based on Quantity, Vapor Pressure, and
               Carcinogenic Potency

          The 96 compounds are scored and ranked on the basis of quantity, vapor pressure,
     and carcinogenic potency using the following  equation:

                        SCC =   (FR/MW)(SF)(VP)                              (TV-3)

     where:
          SCC      =   surrogate chemical score for carcinogens
          FR       =   feed rate
          MW     =   molecular weight
          SF       =   inhalation slope factor
Volume V
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         VP       =   vapor pressure

         Feed rates for individual waste stream constituents are estimated based on waste
     quantities projected for the first year of operation of the WTI facility, as described in
     Appendix HI-1.  Slope factors are obtained from IRIS (1995) and HEAST (U.S. EPA
     1994d).  Nineteen of the 96 compounds have slope factors.  Chemicals for which  SFs
     are not available are not included in this step, but are included in Step 2.  Vapor
     pressures and molecular weights are obtained from several sources, including Howard
     (1993), the National Library of Medicine's Hazardous Substance Data Bank (HSDB),
     Montgomery and Welkom (1990), and the Kirk-Othmer Encyclopedia of Chemical
     Technology (Grayson  1984).
         Four surrogate chemicals,  which are listed in Table TV-5, are selected on the basis
     of the SCC score.  These compounds are selected so as to account for at least 90 percent
     of the total surrogate chemical  score for carcinogens, as indicated in Table IV-5.

     Step 2:   Selection of Chemicals Based on Quantity, Vapor  Pressure, and
              Noncancer  Toxicity

         The 96 compounds are scored and ranked on the basis of  quantity,  vapor pressure,
     and  the potential to cause noncarcinogenic health effects using the following equation:

                       SCNC      =   (FR/MW)(VP)/(RAC)
     where:
         SCNC     =   surrogate chemical score for chemicals with non-cancer chronic
                       toxicities
         FR       =   feed rate
         MW      =   molecular weight
         RAC     =   reference air concentration
         VP       =   vapor pressure

         Feed rates, vapor pressures, and molecular weights for individual waste stream
     constituents are estimated, using the methods described earlier. Inhalation and oral
     reference doses, to estimate RACs, are obtained from IRIS and HEAST (U.S. EPA
                                                             >•'
     1994d); values were available for 51 chemicals.  Chemicals for which RfDs are not
     available are not included in this step.
Volume V
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          Nine surrogate chemicals (two of which were selected in the previous step as
     carcinogens), which are listed in Table IV-6, are selected on the basis of the SC^C
     score.  These compounds are selected so as to account for at least 90 percent of the
     total surrogate chemical score for chemicals  with non-cancer chronic toxicities. as
     indicated in Table IV-6.  In total, 11 chemicals are identified as surrogates for the
     quantitative evaluation of fugitive emissions, as listed in Table IV-7.
          Appendix V-4 provides a list of the 96  organic compounds considered, vapor
     pressures, slope factors, reference doses, and feed rates used in calculating SCC and
     SCNC scores.

     2.    Estimation of Chemical-Specific Fugitive Organic Vapor Emission Rates
          Total fugitive emission rates are estimated in Volume HI for four organic vapor
     sources based on fugitive emissions models,  waste feed throughput, and U.S. EPA-
     derived emission factors, as summarized in Table IV-8. Chemical-specific emission
     rates from one of these sources, tanks in the tank farm that are vented to the CAB
     system, are estimated using U.S. EPA's tank calculation program known as TANKS2.
     The TANKS2 program uses parameters such as molecular weight, vapor pressure over
     a range of temperatures,  and chemical-specific feed rates to derive emission rates.  The
     program requires chemical-specific information on the 11 surrogate chemicals, as well
     as data on the physical properties  of the remainder of the waste feed.  To  represent the
     remainder of the waste feed, it is  assumed to be primarily composed of the 12
     constituents present in the highest volume, as determined from the waste profile for the
     first year of operation1. The waste feed throughput to these tanks is based on the
     maximum heat input rate based on the design of the incinerator (121 million BTU/hr
     higher heating value [HHV]; ENSR 1993).  The resulting total tank farm-related
     emissions from the CAB  system are estimated to be 212.2 Ibs/year,  as shown in Table
     IV-8.  The TANKS2 program also provided an estimate of the emissions represented by
     each of the surrogate organic chemicals, as summarized in Table IV-9.  It should be
     noted that the vapor pressure for dichlorodifluoromethane is beyond the acceptable
     range permitted by the TANKS2 program, so an emission rate is not developed for this
     compound.  However, as evident from the SCNC score for dichlorodifluoromethane
     (Table IV-6), this compound is estimated  to constitute only approximately eight percent
     of the fugitive risk associated with the compounds with noncancer effects.
    1 Waste feed properties are assumed to be reflective of the 12 constituents that comprise
approximately 60 percent of the waste feed. The surrogate chemical emission rates are not
expected to be very sensitive to the overall waste feed properties.
Volume V
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           The results of the tank farm modeling are extrapolated to the other emission
      sources by assuming that the chemical composition of fugitive emissions (expressed as a
      weight fraction) will be the same for all the identified fugitive emission sources.  Thus.
      weight fractions of individual constituents derived from the above analysis of tank farm
      emissions are used with estimates of total fugitive emission rates  (Table IV-8) for each
      of the sources of fugitive organic emissions in determining chemical-specific emission
      rates. Weight fractions in the vapor phase for each of the surrogate chemicals are
      determined using the chemical-specific emission rates summarized in Table IV-9 and the
      total predicted tank farm-related emission rate of 212.2  Ibs/yr, and are summarized in
      Table IV-10.
           The chemical-specific fractions in Table IV-10 are multiplied individually by the
      total estimated emission rates for each of the fugitive organic vapor emissions sources
      identified in Table FV-8.  Thus, chemical-specific emission rates for each of the four
      sources are estimated and are summarized in Table IV-11. It  should be noted that since
      the waste water tank contains highly diluted wastes, use of this procedure of deriving
      chemical-specific emission rates will significantly overstate actual emissions from  the
      waste water tanks.  Total fugitive emissions, however, should  not be significantly
      overestimated because fugitive emissions from the waste water tank account for only a
      small fraction (less than 10 percent)  of the total fugitive emissions from the facility.

     3.   Estimation of Chemical-Specific Emission  Rates  in Fugitive  Ash
               Emissions of specific substances contained within the fugitive ash are
     estimated based on the available data on ash composition.  WIT collects daily samples
     of ash from hoppers associated  with  the air pollution control equipment.  The samples
     are pulverized, blended, and the material is submitted for laboratory analysis.  The
     analytical methods used include SW-846, 8240,  6010, 7471, and 7741 (U.S. EPA
     1994i), depending on the types of wastes fed to the incinerator prior to sample
     collection.  Analytical results from 12 samples collected monthly in  1994 were reviewed
     to estimate average concentrations of constituents  in the  fly ash. The samples of fly ash
     were analyzed by WTI for 80 volatile and semi-volatile organic compounds, total and
     amenable cyanide, and 9 metals.  None of. the 12  samples  indicated detectable levels of
     any of the 80 organic compounds (detection limits for the substance analyzed are
     provided in Table IV-12).  Organic compounds, therefore, are  not evaluated further in
     the analysis of fly ash emissions.
          Average metal concentrations associated with the fly ash are  estimated based  on
     the morthly sampling results, shown  in Table IV-13.  In estimating average
     concentrations, it is assumed that metals that were detected on at least one occasion are
Volume V
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     present in the ash at one-half the detection limit on other occasions when the
     concentrations are reported to be below the detection limits.
          To estimate metal-specific emission rates, the concentration of each metal (or
     inorganic analyte in the case of total cyanide) is multiplied by the estimated fugitive ash
     emission rate of 4.03 x 104 g/sec (estimated in Volume HI). The resulting metal-
     specific emission rates  due to fugitive ash releases are summarized in Table IV-13.

D.   Uncertainties
     In selecting chemicals for quantitative evaluation, it is possible that some are eliminated
from consideration (e.g., because of a lack of toxicity values) that may pose-a potential
health risk.  The process described in this chapter was developed to reduce the uncertainty
associated with this step.  However,  there are several key assumptions, which are shown in
Table FV-14, that may affect the outcome of this assessment.  Most importantly, the selection
of Kw values from the range of values reported in the literature could have a significant
impact on whether a chemical  is selected as a surrogate. In this assessment,  a conservative
method is used  in selecting K^ values; therefore,  as indicated in Table IV-14, it is possible
that an overestimate of risks (associated with organic compounds) may result.
     The following sections  provide a qualitative summary of the uncertainties associated
with the methodologies discussed in this chapter.

     1.    Uncertainties Associated with the Selection of Surrogate Organic Chemicals in
          Stack and Fugitive  Emissions
          There are some uncertainties introduced in condensing the hundreds of chemicals
     present in  emissions from the facility to a smaller list of surrogate chemicals that are
     quantitatively evaluated.  A scoring procedure was designed taking into consideration
     the key factors influencing risk in order to select chemicals most likely  to account for
     the majority of the risk.  The chemicals selected in this process, such as the dioxins and
     furans and the polyaromatic hydrocarbons, have been previously recognized as being
     key chemicals in the risk  assessment of hazardous waste combustion sources (U.S. EPA
     1994a).  Thus, the scoring process was successful in identifying the key constituents for
     this analysis.  It should be recognized,  however, that the chemical-specific and site-
     specific parameters used in the surrogate selection process (as well as many other
     chemical- and site-specific parameters) are used in complex equations in the risk
     assessment.  Consequently, the relative scores estimated using the ^coring algorithm do
     not necessarily reflect the relative risks estimated in the risk assessment.
Volume V
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      2.   Uncertainties Associated with Estimating Chemical-Specific Fugitive Emission
          Rates
          Uncertainties exist in both the nature and magnitude of fugitive emissions.
      Uncertainties in the chemical nature of fugitive emissions principally arise from
      limitations in the understanding of the waste characteristics of the various fugitive
      emission sources.  For example, it is assumed that emissions from the waste water tank
      are similar in composition to the composition  of emissions from the organic waste tank
      farm.  Furthermore, emissions from the tank farm are estimated assuming the waste
      profile from the first year of operation is typical of long-term facility waste receipts.  In
      contrast with stack emissions, fugitive emissions are more strongly  correlated with the
      chemical composition of the wastes,  so that fluctuations in waste  composition directly
      affect the fugitive emissions.
          Uncertainties in the magnitude of chemical-specific fugitive  emissions arise from
      uncertainties in the estimation of total fugitive emissions for the individual sources as
      described in Volume HE, and the extrapolation of the results of the TANKS2 modeling
      of tank farm emissions to the other sources of fugitive emissions, such as the container
      building and the truck wash.  Since the tank farm is  expected to be  the dominant source
      of fugitive emissions, these extrapolations are  not expected to materially affect the risk
      assessment results.
Volume V                                TV. 11
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TABLE IV-1
Selection of Surrogate Organic Chemicals (Stack Emissions) on the Basis of
Quantity, Carcinogenic Potency, and Bioaccumulation Potential
Chemical
OctaCDF
1.2.3.4.6,7.8-HeptaCDF

2.3.4.6.7.8-HexaCDF

1,2.3 4.7.8-HexaCDF

1.2.3.6,7.8-HexaCDF

1 2,3.4.6 7.8-HeptaCDD

2.3,4,7. 8-PentaCDF
Dibenz(a.h)anthracene"
1.2.3.4,7,8.9-HeptaCDF

1.2.3,7.8.9-HexaCDD
1.2.3.7,8.9-HexaCDF
1.2.3.4.7.8-HexaCDD

Benzo(a)pyrene"
1.2.3,6.7.8-HexaCDD

OctaCDD
1.2.3.7.8-PentaCDD
lndeno( 1 ^.S-cdjpyrene'
1.2.3.7.8-PentaCDF
Bis(2-ethylhexyl)phthalate
2,3,7,8-TetraCDD-
Hexachlorobenzene'
Benzo(b)fluoranthenea
Heptachlorobiphenyl*
Heptachlor*
2,3,7.8-TetraCDF
Total of Surrogate Chemicals
Total of 191 Chemicals
Emission
Rate
(g/s)
1.89e-08
9.30e-09
1.50e-09
1.43e-09
1.33e-09
1.24e-09
4.67e-10
5.50e-06
1.22e-09
1.09e-10
2.93e-10
8.95e-ll
5.50e-06
1.66e-10
6.15e-09
6 78e-l)
5.50e-06
3 45e-10
3 72e-05
1.08e-ll
5.50e-06
5.50e-06
1 40e-08
5.50e-07
8.77e-ll
-
-
Slope Factor
(mg/kg/day)"1
1.50e+02
1.50e+03
1.50e+04
1.50e+04
1.50e+04
1.50e+03
7.50e+04
7.30e+00
1.50e+03
1.50e + 04
1.50e+04
1.50e+04
7.30e-t-00
1.50e + 04
1.50e + 02
~! 50e+04
7.30e-01
7 50e + 03
1 40e-02
1.50e+05
1 60e-t-00
7 30e-01
7 70e-(-00
4 50e+00
l.50e-t-04
-

IV.
6.31e+08
7.94e+07
2.00e+07
2.00e+07
2.00e+07
1.58e+08
8.32e + 06
4.90e-f06
7.94e+07
6.17e-f07
2.00e+07
6.17e+07
1.29e+06
2.00e+07
3.89e-l-07
4.37e + 06
4 47e-f06
6.17e+06
2.00e-)-07
4.37e+06
7.76e + 05
1.58e + 06
5.01e + 07
1.82e+06
3.39e + 06
-
-
QCB
Score
1.79e-t-03
l.lle+03
4.50e + 02
4.27e+02
4.00e+02
2.95e+02
2.91e + 02
1.97e+02
1.45e+02
l.Ole + 02
8.77e + 01
8.28e+01
5.17e+01
4.96e + 01
3.59e+01
2.22e + 01
1.79e+01
1.59e+01
1.04e + 01
7.07e-(-00
6.83e + 00
6.36e + 00
5.40e + 00
4.50 + 00
4.46e+00
5.62e+03
5.63e+03
Cumulative
<7c of Total
31.S7<7
51.56*7
50.57TC
67.15^
74.259-r
79.4"^
84 669-f
88.1 5 9"r
90.749-r
92.53%
94.097r
95.56%
96 48%
97.36%
97.99%
98.39%
98.71%
98.99%
99.18%
99.30%
99.42%
99.54%
99.63%
99.71%
99.79%
-
-
Notes
a * Compound not detected in stack gas Estimated emission rate based on half of the lowest detection limit for thi1*
compound
QCB - Quantitv/carcinogenic potency/bioaccumulaiionpoieniial score '
Volume V
-------
TABLE IV-2
Selection of Surrogate Organic Chemicals (Stack Emissions) on the Basis of
Quantity, Noncarcinogenic Potency, and Bioaccumulation Potential
Chemical
H exachl orophene"
Hexachlorocyclopentadiene'1
Bis(2-ethylhexyl)phthalateb
Hexachlorobutadiene"
Di(n)octyl phthalate"
Carbon tetrachlorideb
Total of 191 Chemicals
Emission Rate
(g/s)
3.20e-05
5.50e-06
3.72e-05
l.Ole-04
5.50e-06
1.58e-04
-
Reference
Dose
(mg/kg/day)
3.00e-04
2.00e-05
2.00e-02
2.00e-04
2.00e-02
7.00e-04
-
iv.
3.47e+07
2.45e-(-05
2.00e+07
6.46e+04
1.15e+08
5.37e+02
-
QNB Score
3.70e + 06
6.75e+04
3.71e + 04
3.26e+04
3.16e+04
1.21e+02
3.90e-f-06
Cumulative
<-«: of Total
Q4.Q4T-
9t>.67rf
P".62f7
9S.46^r
99.279r
-
-
Notes
a - Not detected in August 1994 PIC testing, emission rate based on worst-case DRE applied to chemical composition m wasic
feed developed from waste profile information
b - Emission rate based on results of the August 1994 PIC testing.
QNB - Quantiry/noncancertoxicity/bioaccumulation potential score.
Volume V
-------
                                            TABLE IV-3
                                 Surrogate Chemicals Selected for the
                              Indirect Risk Assessment of Stack Emissions
                              PICs and Residual Organic Compounds (15)
   Bis(2-ethylhexyl,)phthalate
   Carbon tetrachloride
   Di(n)octyl phthalate
   Heptachlor
   Hexachlorobenzene
   Hexachlorobutadiene
   Hexachlorocyclopentadiene
   Hexachlorophene
Benzo(b)fluoranthene
Benzo(a)pyrene
Dibenz(a.h)anthracene
Indeno(1.2,3-cd)pyrene
Heptachlorobiphem 1
Hexachlorobiphenyl
Tetrachlorobiphenyl
        Dioxin Congeners (7)
                     Furan Congeners (10)
           2,3,7,8-TCDD
          1,2,3,7,8-PeCDD
         1,2,3,4,7,8-HxCDD
         1.2,3,6,7,8-HxCDD
         1,2,3,7,8,9-HxCDD
        1,2,3,4,6,7,8-HpCDD
              OCDD
        2,3,7,8-TCDF
       1,2,3,7,8-PeCDF
       2,3,4,7,8-PeCDF
      1,2.3.4,7,8-HxCDF
      1.2.3.6,7,8-HxCDF
      1.2,3,7,8,9-HxCDF
      2,3,4,6,7.8-HxCDF
     1,2,3.4.6,7,8-HpCDF
     1,2,3.4,7.8.9-HpCDF
            OCDF
                                             Metals (13)
             Antimony
              Arsenic
              Barium
             Beryllium
             Cadmium
    Chromjum (hexavalent)
            Lead
          Mercury*
            Nickel
          Selenium
            Silver
           Thallium
             Zinc
  Notes
   a  -     Includes methylmercury in aquatic environments
   CDD - chlorodibenzo-p-dioxin
   CDF - chlorodibenzoftiran
Volume V
-------
TABLE FV -4
Fraction of Substance Partitioning onto Particulate Matter
Chemical
Fraction Partitioning
onto Particulate Matter
D5oxin\Furan Congeners
2,3,7.8-TCDD
1,2.3,7.8-PeCDD
1,2.3.4,7.8-HxCDD
1.2.3,6. 7.8-HxCDD
1, 2,3,7. 8.9-HxCDD
1,2,3,4,6, 7, 8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3,7.8-PeCDF
2.3,4,7. 8-PeCDF
1. 2,3.4.7, 8-HxCDF
1.2.3,6.7.8-HxCDF
1,2.3,7.8.9-HxCDF
2,3.4,6,7, 8-HxCDF
1,2.3,4. 6,7, 8-HpCDF
1,2.3.4, 7, 8,9-HpCDF
OCDF
0.449
0.741
0.925
0.964
0.981
0.980
0.998
0.291
0.583
0.697
0.941
0.936
0.892
0.933
0.957
0.975
0.998
PICs and Residual Organic Compounds
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
Carbon tetrachloride
Dibenz(a,h (anthracene
Di(n)octyl phthalate
Heptachlor
H exachl orobenzene
Heptachlorobiphenyl
Hexachlorobiphenyl
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
Tetrachlorobiphenyl
0.673
0.028
0.751
0.000
1.000
0.003
0.000
0.000
0.000
0.000
0.000
0.000
1.000
1.000
0.066 **
Metals
Mercury
0.000
Volume V
-------
TABLE IV-5
Selection of Surrogate Chemicals (Fugitive Emissions) Based on Quantity .
Vapor Pressure, and Carcinogenic Potency
Chemical
2-Nitropropane
Formaldehyde
1 , 1 -Dichloroethene
Hydrazine
Feed
Rate
(kg/yr)
145.854
45.666
22.370
17,423
Molecular
Weight
(g/g-mol)
89.1
30.0
97.0
32.1
Slope
Factor
(mg/kg-d)1
9.4
4.5 x 10:
1.2
17
Vapor
Pressure
(mm Hg)
20
3.883
591
14.4
SCC
6.8 x 105
5.9 x 10-'
3.6 x 10'
2.9 x Itf
Cumulative
Percent of
Total SQ
32. f
60.8
7S.1
92.2
Notes
SCC - Surrogate chemical score for carcinogens.
Vnli
-------
TABLE IV-6
Selection of Surrogate Chemicals (Fugitive Emissions) Based on Quantiu ,
Vapor Pressure, and Noncancer Chronic Toxicitv Potency
Chemical
Acrylonitrile
Carbon Tetrachloride
Pyridine
Formaldehyde
Carbon disulfide
Dichlorodifluoromethane
Dibromomethane
1 , 1 -Dichloroethene
Acetone
Feed
Rate
(kg/yr)
24,611
47,303
160,578
45,666
20,705
26,676
15,297
22,370
252,132
Molecular
Weight
(g/g-mol)
53.1
153.8
79.1
30.0
76.1
102.9
187.9
97.0
58.1
RAC
Gtg/m3)
0.5
0.61
0.88
175
2.5
50
0.05
7.9
88
Vapor
Pressure
(mm Hg)
107.8
113.8
20
3.883
297
5.013
14
591
231
scvc
2.2 x 10-
1.3 x 10s
l.Ox 10'
7.4 x 104
6.8 x 104
5.7 x 104
5.0 x 104
3.8 x 104
2.5 x 104
Cumulative
Percent of
Total SCV
2e>.2
41.1
53.2
62.1
70 1
7t> 9
82.9
87.4
90 4
Notes
RAC - Reference air concentration, estimated to be 25 % of the RfC
SCNC - Surrogate chemical score for chemicals with noncancer chronic toxicities
Volume V
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                                           TABLE IV-7
                         Surrogate Chemicals Selected for the Assessment of
                                  Fugitive Organic Vapor Emissions
                      Acetone
                    Acrylonitrile
                  Carbon Disuifide
                Carbon Tetrachloride
                  Dibromotnethane
Dichlorodifluoromethan;;
   l.]-Dichloroethene
    Formaldehyde
      Hydrazine
    2-Nitropropane
       Pvridine
Volume V
-------
TABLE IV-8
Estimated Total Fugitive Organic Vapor Emissions Rates
Source
Tank Farm Building*
Wastewater Tank
Truck Wash Building
Carbon Adsorption Bed System (total)
From Tanks:
Blending
Holding
Pumpout
Reception
From Container Processing
Total All Sources:
Estimated Emissions
Ib/yr (g/sec)
2.126 (3.0t- x 10:>
202 (2.91 x 10-1)
9.9(1.42 x l(n
224.3 (3.23 x 10'3)
212.2 (3.06 x 10°)
57.2 (8.23 x 10-)
57.2 (8.23 x 10"1)
47.7 (6.86 x 10-1)
50.1 (7.21 x 10J)
12.1 (1.74x 10-4)
2,562 (3.68 x 10-)
Noles
a - Tank farm building emissions are from the l&aky valves and flanges which, for the purposes of this nsk assessment, are
assumed to all occur from the vents on the roof of this building
Volume V
-------
TABLE IV-9
Estimated CAB Emissions Associated with the
Organic Waste Tanks
Surrogate
Chemical
Acetone
Acrylonitrile
Carbon Disulfide
Carbon Tetrachloride
Dibromomethane
1 , 1 -Dichloroethene
Formaldehyde
Hydrazine
2-Nitropropane
Pyridine
Estimated Emissions
(g/sec)
1
16
2.57
7
67
5.15
-1
7
6
1
2
2
53
53
38
63
11
68
x
X
X
X
X
X
X
X
X
X
10-'
io-?
io-<
io-5
10*
io-5
10J
10-*
10-'
io-5
Note
The vapor pressure of dichlorodifluorumethane was beyond
the acceptable range of values for the TANKS2 program and
an emission rate could not be developed
Volume V
-------
TABLE IV-10
Estimated Fraction of Total Emissions Due to
Individual Surrogate Chemicals
Surrogate
Chemical
Acetone
Acrylonitrile
Carbon Bisulfide
Carbon Tetrachloride
Dibromomethane
1 , 1 -Dichloroethene
Formaldehyde
Hydrazine
2-Nitropropane
Pyridine
Fraction of Total
Emissions
0.38
0.0084
0.025
0.017
0.0008
0.025
0.21
0.0005
0.0069
0.0088
Note
The vapor pressure of dichlorodifluoromethane was bevond
the acceptable range of values for the TANKS2 program and
an emission rate could not be developed
Volume V
-------
TABLE IV-11
Estimated Emissions of Surrogate Chemicals from
Fugitive Organic Vapor Emissions Sources
Chemical
Acetone
Acrylonitrile
Carbon Disulfide
Carbon Tetrachloride
Dibromomethane
1 . 1 -Dichloroethene
Formaldehyde
Hydrazine
2-Nitropropane
Pyridine
Estimated Emissions (g/sec)
CAB System
1.23 x 10'3
2.71 x 10 5
S.lOx 10 5
5.44 x 105
2.68 x 10"*
7.95 x 10'5
6.75 x 10-
1.72 x 10-*
2.23 x 10-5
2.83 x 10 5
Wastewater Tank
l.lOx 10"
2.44 x 10s
7.30 x JO'5
4.90 x ID'3
2 41 x 10^
7.16x 10'5
6.08 x 10-1
1.55 x 10-6
2.01 x 10'5
2.55 x ID'5
Truck Wash
5.41 x 10s
1.19x 10"
3.58 x 10-*
2.40 x 10*
1.18 x lO'7
3.51 x lO*
2.98 x 10s
7.58 x 10-*
9.86 x lO'7
1.25x 10^
Tank Farm
1 lt> \ 10 :
2.57 x 10~
7.6S ,\ 10-
5.16 \ 10~
2.54 x 10 '
7.54 \ 10-"
6.40 \ 10 •"'
1.63 x 10"
2.12 x 10-
2.68 x 10J
Nole
The vapor pressure of dichlorodifluoromethane was beyond the acceptable range of values for the TANKS2 program and an
emission rate could not be developed
Volume V
-------
Table IV-12
Detection Limits Used in Analysis of ESP Fivash Samples
Substance
Practical
Quantitation Limit"1
(ppm)
Organic Compounds
Acetone
Acetophenone
2-Acetylamino-fluorene
Aniline
Aroclor 1016
Aroclor 1221
Aroclor 1232
Aroclor 1242
Aroclor 1248
Aroclor 1254
Aroclor 1260
Benzene
Benzo[a]pyrene
BisC2-chloroisopropyl (ether
Bis(2-ethylhexyl)phthalate
N-Butyl alcohol
Carbon tetrachloride
Chlorobenzene
Chlordane
Chloroform
Chloromethane
2-Chloronaphthalene
m-Cresol
o-Cresol
p-Cresol
Chrysene
2.4-D
1 ,2-Dibromoethane
Dibromethane
1 .2-Dibromo-3-chloropropane
m-Dichlorobenzene
o-Dichlorobenzene
p-Dichlorobenzene
50
1
50
-I
0.5
0.5
0.5
0.5
0.5
0.5
0.5
1
10
5
5
-»
->
T
0.1
">
25
->
->
~t
-i
5
5
5
i
5
~>
i
i
Volume V
-------
Table IY-12 (continued)
Detection Limits Used in Analysis of ESP Flyash Samples
Substance
1 . 1 -Dichioroethane
1,2-Dichloroethane
1 , 1 -Dichloroethylene
Dimethylphthalate
Di-n-butylphthalate
Di-n-octylphthalate
1 ,4-Dioxane
Endrin
Ethyl acetate
Ethylbenzene
Ethyl ether
Hexachlorobenzene
Isobutanol
Lindane
alpha-BHC
bela-BHC
delta-BHC
Methoxychlor
Methylethyl ketone
Methylisobutyl ketone
Methylene chloride
Naphthalene
•Nitrobenzene
Pentachlorobenzene
Pentachloronitrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Pyrene
Pyridine
1 ,2.4,5-Tetrachlorobenzene
1,1,1 ,2-Tetrachloroethane
1 , 1 ,2,2-Tetrachloroethane
Tetrachl oroethy lene
Practical'
Quantitation LimitJ
(ppm)
^
->
10
25
3
" 25
50
0.08
10
5
50
•^
50
0.04
0.1
0.1
0.1
0.09
10
10
10
0.8
10
^
">
5
0.8
->
0.8
i
">
5
5
2
Volume V
-------
Table IV-12 (continued)
Detection Limits Used in Analysis of ESP Flvash Samples
Substance
Toluene
Toxaphene
2.4.5-TP
1 .2,4-Trichlorobenzene
Trichloroethylene
1,1,1 -Trichloroethane
1,1,2-Trichloroethane
Trichlorofluoromethane
1 , 1 ,2-Trichloro-l ,2,2-trifluoroethane
Xylene
Carbon disulfide
Cyclohexanone
Methanol
Practical
Quantitation LimitJ
(ppm)
10
o.s
5
1
->
•^
*1
10
10
10
90
15
15
Inorganic Compounds
Total Cyanides
Amenable Cyanide
Arsenic
Barium
Cadmium
Chromium
Lead
Mercury
Nickel
Selenium
Silver
0.5
0.5
2.5
1
0.01
0.5
0.5
0.05
0.15
0.1
0.03
Note
a - Detection limits specified by laboratory
Volume V
-------
TABLE IV-13
Estimated Average Concentrations of Metals and Inorganic Compounds
in Fugitive Flv Ash Emissions
Metal/Inorganic
Compound
Arsenic
Barium
Cadmium
Lead
Nickel
Selenium
Silver
Total Cyanide
Frequency
of Detection
1/12
9/12
11/12
11/12
9/12
5/12
6/12
2/12
Concentration
Range (mg/kg)
<0.5 - 27
<1 -4.1
<0.1 -640
<0.5 - 130
<0.15 - 1.9
<0.1 - 1.0
<0.1 - 2.1
<0.5 - 1.1
Average
Concentration
in Ash (mg/kg)
3.4
1.7
71.0
36.1
0.7
0.2
0.3
0.4
Emission Rate
(g/sec)
1.37 x \Q*
6.75 x 10"
2.86 .\ 10'
' 1.45 x 10"
2.92 x 10-"
8.23 x 10-V
1.04 x ID'"
1.41 x 10"
Notes.
< - Lower end of concentration range is the lowest detection limit from samples in which analvte was not detected
Volume V
-------
TABLE IV-14
Key Assumptions for Chapter IV
(Selection of Surrogate Chemicals)
Assumption
The screen to select surrogate organic stack chemicals
retains the chemicals that present the greatest health
risk. The more conservative (oral or inhalation)
toxicity value is used.
Kim is an accurate measure of bioaccumulation
potential. The K,TO values are appropriate
The screen to select surrogate organic fugitive
chemicals retains the chemicals that present the greatest
health risk.
Basis
Professional judgment. Ilie screen was designed to retain
the chemicals that contribute most significantly to risk and
includes several compounds to ensure chemicals with
lower rankings were not inadvertently overlooked.
Professional judgment. Measurement of K,,w values,
especially for highly lipophtlic chemicals, contains
significant uncertainty. Maximum values were selected
for the assessment. For example, the K,)W value for bis(2-
elhylhexyljphthalate significantly overestimates its
bioaccumulation potential
Professional judgment. The variables used in the
screening process have the greatest impact on estimated
risks.
Magnitude
of Effect
low
high
low
Direction of
Effect
unknown
likely
overestimate
unknown
Notes
low = less than a factor of two
medium = a factor of two to ten
high = greater than a factor of ten
Volume V
!V-27
-------
                    V.  IDENTIFICATION OF EXPOSURE
                       POPULATIONS AND PATHWAYS
 A.   Introduction
      The exposure assessment step of the risk assessment process involves the identification
 of the potentially exposed population, and the measurement or estimation of the magnitude of
 exposure to individuals in that population.  This chapter and the following two chapters
 present the steps used in assessing exposure to the population in the vicinity of the WTI
 facility.  Within the exposed population, the magnitude of exposure is expected to van- by
 individual, due to differences in individual characteristics and activity patterns, among other
 factors.  Therefore, a distribution of exposures across the population exists.  Direct
 measurement of this exposure distribution cannot readily  be performed.  Therefore.
 subgroups within the population are identified that are expected to have similar exposure
 because of similarities in activity and behavior patterns.  This chapter describes the
 approaches used to identify the exposed population, subgroups within that population, and
 pathways of exposure; the following chapters provide estimates of environmental
 concentrations based on  the fate and transport of chemicals in the environment, and estimates
 of human exposure of local populations to substances in affected environmental media.
     In the WTI Risk Assessment Project Plan (U.S. EPA 1993b),  a number of preliminary
 population subgroups were identified.  During the peer review process of the Project Plan,
 several additional subgroups of the exposed population  that may be at a higher risk due to
 behavior patterns, proximity to the facility, or sensitivity were identified.  The Peer Review
 Panel suggested a number of additional population subgroups for possible consideration in the
 risk assessment.  A review of these subgroups is provided in Appendix V-5.  Based on the
 recommendations of the  Peer Review Panel and the analysis described in Appendix V-5, one
 additional exposure group, deer hunters,  is included in the HHRA.

 B.   Population Subgroups Potentially  Exposed to Stack Emissions
     As stack emissions  from the WTI facility disperse downwind, individuals may be
exposed to these emissions via direct inhalation.  In addition, dry and wet deposition may
occur on soil, surface water, and  vegetation.  The deposited chemicals may then be taken up
by crops, livestock, and fish.  Ingestion of locally raised crops and livestock, and
consumption of fish caught in local streams, lakes, and  rivers  represent potential pathways of
Volume V
-------
indirect human exposure.  Other indirect exposures, such as consumption of local milk and
milk products potentially affected by site emissions, are also possible.
     Based on the characteristic activity and behavior patterns, the follow -ing subgroups have
been identified for the population in the study area  surrounding the WTI facility:

     •    Adult non-farming residents;
     •    Child non-farming residents:
     •    Adult farmers whose diet consists partially of homegrown food products (e.g..
          meat, milk, vegetables);  and
     •    Children of farmers whose diet consists partially of homegrown food products.

     In addition to these subgroups, which are expected to comprise a significant portion of
the local population, three additional potentially exposed subgroups of the population have
been identified.  Individuals in these subgroups may experience elevated exposures to
contaminants from the WTI facility due to their specific behavior pattern. These subgroups
are the following:

     •    Children (7 to 12 years old) who attend school in the area;
     •    Adult farmers whose entire diet is homegrown (referred to as subsistence farmers);
          and,
     •    Children of subsistence farmers.

     In addition to these subgroups, several groups  have been  identified as special population
segments who may be highly exposed because of  their particular activity patterns.   On this
basis, the following subgroups are included in the risk assessment:

     •    Adult and child residents whose diet consists partially of homegrown food
          products;
     •    Breast-feeding infants (assumed to be all  children under 1  year old);
     •    Subsistence fishermen (recreational fishermen who obtain a significant portion of
          their diet from fish in local bodies of water);  and
     •    Deer hunters  who consume deer that have been exposed to contaminants in the
          food chain.

     Exposure is evaluated in this assessment for  the specific activities listed above;
however,  these exposures are expected to  be incremental to exposure experienced through
other pathways by the individual performing the activity.  Exposure from consuming

Volume V                                                                           	
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 homegrown vegetables, for example, applies to only those residents that have home eardens.
 For breast-fed infants and subsistence fishermen, the pathways listed above are likely to be
 the most significant source of exposure and. therefore, risk.  Finally, only a small fraction of
 the population would be anticipated to consume deer meat.

 C.   Potential Exposure Routes for Stack Emissions
      The potential routes of exposure for the population subgroups that may be exposed to
 stack emissions are tabulated in Table V-l and discussed in greater detail in the following
 sections. Inhalation of stack and fugitive emissions is the only direct route of exposure: the
 other routes in Table V-l are indirect exposure routes.

      1.   Air Exposure Routes
          Direct inhalation of emissions from the WTI incinerator stack is the primary  route
     of  airborne exposure for all population subgroups.

     2.   Soil Exposure Routes
          A portion of the chemicals emitted from  the stack is expected to be deposited on
     surface soils in the vicinity of the facility.  Residents working or playing outdoors may
     inadvertently ingest soil, and absorb chemicals through the skin during soil contact.
     These  exposure routes are also assumed to apply to farmers,  who work outdoors for
     significant periods of time, and children who attend local schools and play outdoors.

     3.   Terrestrial Food Chain Exposure Routes
          Chemicals deposited in the vicinity of the facility  may accumulate in  various parts
     of the  food chain.   Chemicals may be incorporated in vegetation, crops, plants, and
     forage, as a result of deposition on leaves, absorption from the soil through the roots,
     and uptake of vapors from the air. Vegetation  may, in turn, be consumed by  local
     residents, or by dairy cows, beef cattle,  pigs, and poultry.  The cows, cattle,  pigs, and
     poultry may also be exposed through ingestion of soil.  Chemicals may then accumulate
     in the meat from the b'vestock and milk from the  cows.  Therefore, consumption of
     vegetables, beef, poultry, pork products, eggs, and dairy  products from local  farms and
     gardens is a potential source of indirect exposure  to stack emissions for humans. Each
     of these food chain  exposures is evaluated in the risk assessment.

     4.    Surface Water Exposure  Routes
          Chemical emissions may enter surface water in the vicinity of the facility through
     deposition of stack emissions directly onto the water body or through runoff of

Volume V                                TT ->
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     contaminated soil that enters the water body.  Although a portion of the drinking water
     for East Liverpool and Columbiana County is supplied from the Ohio River, surface
     water is subjected to  several treatment steps before use: therefore, significant exposure
     through this pathway is unlikely, and is not evaluated quantitatively in this assessment.
          It is possible that local residents may swim in surface water bodies and come into
     contact with chemicals through ingestion and dermal absorption.  A West Virginia
     Department of Natural Resources (Pierce et al. 1983) study has indicated that a
     significant amount of swimming occurs during the summer months in the Ohio River
     near East Liverpool.  This potential route of exposure, therefore, is considered in the
     assessment.  In addition, discussions with a local wildlife official indicated that
     Tomlinson Run Lake, located approximately six miles south of the WTI facilitv.  and
     Little Beaver Creek, located two miles north and east of the WTI facility, are other
     popular recreational areas in the vicinity of the WTI facility.  Exposure to surface water
     in these water bodies is evaluated.

     5.   Breast Milk Exposure Route
          Lipophilic compounds, including dioxins and PCBs,  may accumulate in body
     tissues, preferentially concentrating in adipose tissue.  Such compounds may then
     accumulate in  the breast milk of nursing women in the study area.  Exposure to nursing
     infants of mothers in  the high-end subgroup is considered in the risk assessment.

     6.   Fish Consumption Exposure Route
          Chemicals dissolved in surface water and adsorbed to sediments may be
     transferred to and accumulate in fatty tissues of fish in local water bodies.  Individuals
     may consume fish caught locally and be exposed indirectly to stack emissions.  For
     residents living in the vicinity of the  WTI facility, it is possible that a portion of the fish
     diet may be  derived from local waters, thereby increasing the potential exposure
     through the food consumption pathway.   An analysis of this exposure pathway is
     presented in Appendix V-6.  This analysis indicates that fish caught in the vicinity of
     the WTI facility are not a significant source of food for the typical local  resident.  The
     basis for this assumption is presented  in Appendix V-6.  It should be noted, however,
     that a subgroup of the local population may exist that derives a significant fraction of
     their diet from locally caught fish. This activity is referred to in  this assessment  as
     subsistence fishing.  Although no data or information are available tp indicate that
     subsistence fishermen actually reside in  the vicinity of the WTI facility, exposure to
     WTI-related contaminants by subsistence fishermen will be considered in the risk
     assessment as a high-end exposure scenario.
Volume V
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     7.   Groundwater Exposure Route
          It is possible that chemicals deposited on surface soils could become dissolved in
     precipitation and percolate through surface soils to the groundwater.  The Methodology
     for Assessing Health Risks Associated with Indirect Exposure to Combustor Emissions
     (U.S. EPA  1990a), evaluated the likelihood of this route of chemical transport using
     worst-case assumptions in a leachate transport model  for organic and inorganic
     constituents. U.S. EPA concluded that a very limited potential for contamination of
     groundwater exists, and that  further evaluation of this pathway was unnecessary.  The
     groundwater exposure pathway, therefore,  is not considered in this assessment.

D.   Population  Subgroups Potentially Exposed to Fugitive Emissions
     As  noted in Volume HI, fugitive emissions occur in the form of organic chemical
vapors and as ash. The fugitive vapor emissions are comprised almost entirely of organic
compounds that volatilize from drums, tanks, valves,  etc.,  and are transported off-site by
wind.  Because of the nature of these fugitive emissions, i.e., volatile organic compounds,  it
is assumed that inhalation would be the primary exposure pathway.  Deposition of organic
vapors is generally considered to be  insignificant and  is, therefore, unlikely to result in
human health risks through indirect routes of exposure. In addition, as described in Volume
HI, fugitive vapor emissions primarily occur from ground-level sources  (with the exception
of the CAB system).  The most  significant impacts from ground-level sources are likely to
occur in  the immediate vicinity of  the source. The primary exposed populations in the
vicinity of the WTI facility, therefore, include residents (adults and children) that generally
live to the north and west of the facility. Because of the commercial/industrial location of
the WTI  incinerator and the lack of farms in the immediate vicinity, significant exposure by
farmers to fugitive emissions is not expected to occur.  Therefore,  in this assessment, risks
due to fugitive vapor  emissions via inhalation are estimated for three population subgroups:

     •   Adult non-farming residents;
     •   Child non-farming residents; and
     •   Children (7 to 12 years  old) who attend school in the area.

     Fugitive ash emissions, which are also  released from a near ground-level source, will  be
dispersed to a limited degree with  the most significant  impacts likely occurring in the vicinity
of the source.  Because the ash is in  particle  form, deposition and subsequent exposure to
individuals  in the vicinity of the  WTI facility by indirect exposure pathways must be
considered.  Therefore, risks associated with direct and indirect exposure to fugitive ash
emissions are estimated for the three population subgroups  noted above.  The indirect

Volume V                                 w c
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 pathways of exposure that are considered include ingestion of and dermal contact with soil.
 and ingestion  of homegrown vegetables.  As noted earlier, farming is not presently conducted
 in the immediate vicinity of the facility, nor is it expected that farming will be conducted in
 this area in the near future.

 E.   Uncertainties
     In developing the scope of the HHRA, some assumptions are made in order to focus the
 assessment on the most important exposure pathways and populations, thus reducing the
 complexity of the assessment.  In doing so,  it is possible that all risks associated with  the
 WTI facility may not be accounted for; however, given the conservative nature of this
 assessment, it is unlikely that risks are underestimated.  The key assumptions used in
 identifying exposure populations and pathways are summarized in Table V-2 along with a
 rationale and qualitative  descriptions of their potential effects on estimated risks.  The  key
 assumptions used in identifying exposure populations and pathways are not expected to
 impact the results of the HHRA significantly (i.e., the magnitude of effect  is "low" for both
 assumptions).

     1.   Uncertainties in the Identification of Exposure Populations
          In this assessment, an attempt is made to identify subgroups within the exposed
     population in the vicinity of the WTI facility that have similar behavior patterns and.
     therefore, have similar levels of exposure.  To this end, a range of exposure populations
     are identified that include  infants, young  children, school-age children, and adults (both
     farming and non-farming). It is possible, however, that a group of individuals may
     exist that are more  highly  exposed than any of the identified population subgroups.
     Consequently, exposure to such individuals would be underpredicted.
          As noted above, several potential  high-end  exposure populations  were suggested
     for consideration as potential high-end exposures. After careful  review, however, it  did
     not appear that any of the  groups  are either highly exposed or exposed significantly
     different  from populations already  identified.  Therefore, it does not appear that a
     significant underestimate of risks has resulted from the process used to identify
     exposure populations.

     2.    Uncertainties  in the Identification  of Exposure Pathways
          The exposure pathways identified  in this chapter cover a wide range of possible
     activities likely experienced by individuals in the local population. There are several
     potential  exposure pathways that are not quantitatively evaluated  in this assessment,
     including primarily  exposure to groundwater (through consumption, dermal contact, or

Volume V                                 -- -
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      inhalation during showering) and exposure to surface water used by local municipalities
      for drinking water.  The groundwater exposure pathway is not considered because based
      on existing information, it would not appear to be a source  of significant risks to the
      local population.
          Surface water (the Ohio River) is used as a source of drinking water in the East
      Liverpool area.  Although this water is treated (including flocculation and
      sedimentation, sand filtration, carbon absorption,  and chlorination)  before use b\  local
      residents, it is possible that some types of contaminants (e.g., dioxins and heav\ metals)
      may not be entirely removed.  Based on  the results of the surface water-related
      exposure pathway (Chapter VITJ), however, the use of the Ohio River as a drinking
      water source would not appear to present a significant source of risk.
          As described in Appendix V-6, consumption of locally-caught fish by residents is
      not considered in this assessment.  Certain individuals within the population may be
      exposed by this pathway,  but it is estimated that,  on average, risks  by this pathway to a
      resident are insignificant.   To account for potential risks to individuals who consume
      fish from local waters, risks to the subgroup referred to as subsistence fishermen are
      estimated.  Based on the insignificant risks estimated for this pathway (Chapter VIE), it
      is estimated that risks to residents due to consumption of fish from  local waters are also
      insignificant.
Volume V
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TABLE V-l
Exposure Populations and Pathways Considered in the Risk Assessment
Exposure
Pathway
Air Inhalation
Soil Ingestion
Dermal Contact with Soil
Local ly Raised Meal
Milk and Milk Product1; from
lx>calU Raised Cows
Homegrovui Vegetables
Surface Water Ingestion
Dermal Contact with Surface Water
Exposure Population
Resident
Adult
X
X
X
X
X
NAd
X
X
Child3
X
X
X
X
X
NA"
X
X
School
Child"
X
X
X
X
X
NAd
X
X
Farmer
Adnll
X
X
X
X
X
X
X
X
Child"
same as CR
same as CR
same «s CR
X
X
X
same as CR
same as CR
Subsistence Fanner
Adult
same as AF
same as AF
same as AF
X
X
X
same as AF
same as AF
Child"
same as CR
same as CR
same »s CR
X
X
X
same as CR
same as CR
Activites Associated with Potential High-End Exposure Subgroups
Consumption of Homegrown Fruits and Vegetable (Adult and Child Residents and School-age Children)
Consumption of locally Caught Fish by Subsistence Fisherman
Consumption of Mother's Milk by Breast-feeding Infants'
Consumption of Meat from Locally Hunted Deer
Notes a - assumed to he in 1 to 6 year old age range
N A Not applicable h - assumed to he in 7 to 12 year old age ranc
-------
                                                                  TABLE V-2
                                                        Key  Assumptions for Chapter V
                                             (Identification of Exposure Pathways and Populations)
                      Assumption
                                                               Basis
Magnitude of
    Effect
Direction of
   Effect
  Population subgroups and high-end subgroups have
  been adequately identified and characterized (e.g.,
  inclusion of subsistence fisherman is appropriate).
                                       The populations identified include several populations
                                       recommended for inclusion  by the Peer Review Panel
                                       that evaluated the Draft Project Plan for the WTI Risk
                                       Assessment. Inclusion of several high-end subgroups
                                       (e.g.,  subsistence fisherman) likely overestimates risk
                                       because  there are  no data that support the existence of a
                                       subsistence fisherman  and the data suggest that only a
                                       limited subsistence farmer population exists.
     low
overestimate
  Exposure pathways have been adequately identified and
  characterired   'Hie ground water pathway and surface
  water consumption are not assessed
                                       Hxposure pathways are recommended in U.S. EPA
                                       guidance (e.g., U.S.  EPA I989b).  U.S. EPA (199()a)
                                       recommends that evaluation of the ground water pathway
                                       is unnecessary based  on their study using worst-case
                                       assumptions.  The surface water goes through several
                                       treatment steps prior  to use so exposure to chemicals will
                                       be limited.
     low
   variable
  Notes-
  low
  medium
  high
less than a factor of two
a factor of two to ten
greater than a factor of ten
Volume  V
                                                                       V-9
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    VI.  ESTIMATION OF ENVIRONMENTAL CONCENTRATIONS
A.   Introduction
     Individuals living and working in the vicinity of the WTI facility may be exposed to
substances emitted from the facility through both direct and indirect pathways.  Direct
exposure occurs through inhalation of vapors and particles in the air.  Indirect exposure
occurs as a result of dry and wet deposition of particles and vapor onto soil-and vegetation.
and subsequent migration of these chemicals into other media. For example,  stack gas
constituents that are deposited onto the soil can be  incorporated into vegetation, which can
then be ingested by livestock. Consequently, human exposure may occur through ingestion
of vegetables or livestock grown or raised locally.  Additionally, deposition of stack gas
constituents on local water  bodies and runoff from  watershed soils will result  in
concentrations of contaminants in surface water in  the vicinity of the facility.
     In order to assess the  risk of exposure to chemicals emitted from the  stack, an estimate
of the concentrations of substances of potential concern in air, soil, vegetables,  animal
products (e.g.,  meat, eggs, milk, game), surface water, fish, and mothers' breast milk is
necessary.  The modeling of contaminant transport in air is discussed in Volume IV.  For
other environmental media, concentrations are estimated using fate and transport models
designed to simulate the transport of substances in  the environment over time.  The models
used in  this assessment are  based on U.S. EPA guidance (U.S. EPA 1990a, 1993a, 1994c)
and reflect the current understanding of environmental fate and transport processes.  This
chapter  presents an overview of the models used.  A more detailed presentation of the fate
and transport models, input values used in the models, and the basis for these values is
located  in Appendix V-7.
     As noted in Appendix V-7, whenever possible, site-specific data are applied in this
assessment rather than using conservative default values.  Substantial effort has been devoted
to obtaining site-specific information for use in estimating environmental concentrations,
including reviews of the scientific literature and conversations with local biologists and
agricultural agents.  Table VI-1 presents the site-specific values used in this assessment.
     It is anticipated that use of site-specific values reduces the uncertainty associated with
the modeled results.  It should be noted, however,  that several of the podels applied in this
assessment are based on limited data and, therefore, contribute to the uncertainty in the
results.  The uncertainties that result from applying these models are discussed qualitatively
Volume V
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 at the end of this chapter and are evaluated quantitatively in Chapter IX.  To compensate for
 the uncertainty in the estimation process, conservative assumptions are generally applied in
 this assessment so that estimated environmental concentrations are likely to be greater than
 those actually associated with facility operations.

 B.  Estimation of Soil Concentrations
     Stack gas constituents emitted to the atmosphere may deposit on  surface soils in the area
 surrounding the WTI facility due to dry and wet deposition of particles and vapor. The
 concentration of chemicals in surface soil is required to  1) estimate potential human
 exposures through soil ingestion and dermal contact with the soil, 2) predict uptake in
 vegetation for human consumption and grazing animals,  and 3) estimate concentrations in
 surface water due to runoff of contaminated soil.
     To estimate the chemical concentration in soil, the  following equation is used (U.S.
 EPA  1990a):
                    CS  -
                                          (2) (BD)
where:
     CS       =   chemical concentration in soil, mg/kg
     Dyd      =   dry deposition rate for particles, g/m2-yr
     Dyw      =   wet deposition rate for particles, g/m2-yr
     LDJP      =   vapor deposition rate, g/m2-yr
     ks        =   soil loss constant,  yr1
     Tc        =   total time of deposition, yr
     Z         =   soil depth, cm
     BD       =   bulk density, g/cm3

     Soil concentrations are estimated for surface (one centimeter) soils and root zone (20
centimeters) soil (U.S. EPA 1990a).  In addition, soil concentrations within the upper 10
centimeters are estimated as an input to estimating surface water concentrations (U.S. EPA
1994c), assuming an agricultural watershed, which could  have some tilled and some untilled
soils. Estimated soil concentrations at these depths are based on deposition rates of
constituents of concern assuming complete mixing within  the soil layer of interest (1 cm, 10
cm,  or 20 cm) and continuous operation of the facility over a period of 30 years.  Dry and
wet deposition rates for particles (Dyd and Dyw) are predicted by the ISC-COMPDEP
model.
Volume V
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      The parameters values used in the above equation are presented in Appendix V-7 along
 with the methodology and assumptions used in estimating soil concentrations.  Site-specific
 information needed to estimate soil concentrations include: fraction of organic carbon in soil:
 bulk density of soil; annual precipitation, irrigation, runoff, and evapotransporation: soil
 volumetric content; Universal  Soil Loss Equation (USLE) constants for erosivity and
 erodability; wind speed; and air  temperature, viscosity and density.  The values used in this
 assessment are presented in Table VI-1.

 C.   Estimation of Concentrations in Vegetation
      The concentration of constituents in vegetation is necessary to estimate .the exposure to
 chemicals through ingestion of vegetation (i.e., vegetables and fruit) as well as to estimate
 the uptake of constituents in animals that feed on the vegetation (i.e., grain, forage, and
 silage).  Stack gas constituents may bioaccumulate in plants through three mechanisms:
 uptake by roots, direct deposition on exposed plant tissues, and air-to-plant transfer of vapor-
 phase constituents.   These mechanisms are discussed more fully by U.S.  EPA (1990a and
 1994c).
      The magnitude of chemical  uptake by produce is dependent on the type of vegetable and
 its potential for exposure to the atmosphere.   For example, contaminant deposition is more
 likely to occur onto leafy vegetables (such as lettuce) than onto vegetables that are protected
 from the atmosphere (such as corn or root vegetables).  Similarly,  the uptake of chemicals
 from the soil will differ for below ground and above ground vegetables.  Therefore, four
 types of produce classes  are considered in the risk assessment:

      •    Leafy produce (e.g., lettuce,  broccoli,  forage);

      •    Above ground protected produce (e.g.,  com, peas,  grain);

      •    Above ground exposed produce (e.g., tomatoes, green peppers); and

      •    Root produce (e.g., carrots,  onions).

     Assumptions presented in  Appendix V-7, for each of these classes of produce are used
in the following equations to estimate concentrations of chemicals in produce.  The overall
approach and important,  site-specific input parameters are described below; however, details
                                                                  V
on model  application are presented  in Appendix V-7.
     The total concentration of a  constituent in a  given plant (CV) due to root uptake (Pr,),
direct deposition (PdJ, and air-to-plant transfer (PVj) can be calculated as  follows:

Volume V                                -trr ->
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                  CV  =  Pr
                                               Pd. +  P\i
(VI-2)
 where:
     CV   =
     Pr,   =
     Pd,   =
     Pv,   =
total concentration of constituent in the i* plant group, mg/kg
concentration of constituent in i* plant group due to root uptake, mg/kg
concentration of constituent in r* plant group due to direct deposition, mg/kg
concentration of constituent in i* plant group due to air-to-plant transfer.
mg/kg
Root Uptake
     The constituent concentration from root uptake (Pr^ f°r above ground vegetation (i.e..
above ground exposed and protected vegetables, and leafy vegetables) is dependent on the
soil concentration (CS) and a chemical specific plant/soil bioconcentration factor (Br,):
                                    Prt  =
                                                                   (Vl-3)
where:
     Pr,

     CS

     Br,
concentration of constituent in Ith plant group due to root uptake, mg
constituent/kg plant tissue, dry weight (DW)
soil concentration of constituent after the total period of deposition, mg
constituent/kg soil
plant/soil bioconcentration factor for the i* plant group, (mg constituent/kg
plant tissue DW)/(mg constituent/kg soil)
     Baes et al.  (1984) present bioconcentration factors for the metals evaluated in the
HHRA.  For organic chemicals, the bioconcentration factors are calculated using an equation
developed by Travis and Arms (1988) and recommended by U.S. EPA (1993a).  Details on
this equation are presented in Appendix V-7.
     For below  ground vegetation (i.e., root vegetables), Pr, can be estimated by the method
developed by Briggs (1982) as follows (further details in Appendix V-7):
                               Pr.
                                        (CS)  (RCFi} (VGbg}
                                               Kd.
                                                                   (VI-4)
where:
     RCF,
     Kds
     root concentration factor for the i* plant group, L/kg
     empirical correction factor, unitless
     soil/water partition coefficient, L/kg
Volume V
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     Briggs (1982) developed a regression equation dependent on the octanol/water partition
 coefficient, K^, to calculate RCF, values for organic compounds, presented in
 Appendix V-7.
     VGbg is a factor introduced into the calculation  of contaminant concentrations to reflect
 the reduced translocation of compounds in bulky, below ground vegetables, such as carrots
 and potatoes (U.S. EPA 1994c). In general, the contaminant concentrations measured in the
 barley roots of the Briggs (1982) experiments would be representative of the levels of
 compounds in the outer few millimeters of below ground vegetation, but much  higher than
 the average concentration in the whole vegetable.  Thus, a VGbg value of 0.01 is used for all
 substances of concern, as recommended by U.S. EPA (1994a).

 Direct Deposition
     The factors related to the plant concentration attributable to direct deposition on  exposed
 plant tissues (Pdi), as shown in Appendix V-7, are as follows:
                 Pd   .
                      =
where:
     Pd,       =    concentration of constituent due to direct deposition in the Ith plant
                    group, mg constituent/kg plant tissue DW
     Dyd      =    yearly dry deposition rate,  g constituent/m2-yr
     Fw       =    fraction of wet deposition that adheres to plant surfaces,  unitless
     Dyw      =    yearly wet deposition rate,  g constituent/m2-yr
     Rp,       =    interception fraction of the edible portion of plant tissue for the i"1 plant
                    group, unitless
     kp        =    plant surface loss coefficient, yr"1
     Tp,       =    length of plant's exposure to deposition per harvest of the edible portion
                    of the f* plant group, yr
     Yp,       =    yield or standing crop biomass of the edible portion of the r* plant
                    group, kg DW/m2

     Parameter values used in the above equation are presented in Appendix V-7.  The wet
and dry deposition rates are provided from the air dispersion modeling.  Equations to
calculate Rp,, and kp are also presented in Appendix V-7. Values for Tp; and Yp, are
obtained from Pennsylvania Agricultural Statistics Service (PDA 1994) and the Census of
Agriculture (USDC 1993a,b,c), as shown in Table VI- 1.  This route of exposure for plants is

Volume V                                irr  c
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not considered for above ground protected vegetables and root vegetables, which are
significantly less susceptible to direct deposition.

Air-to-Plant Transfer
     Plant concentrations attributable to air-to-plant transfer are dependent on the vapor-
phase air concentration, and an air-to-plant biotransfer factor, as shown in the following
equation.  This type of transfer applies only to above ground exposed plants (i.e., does  not
include root vegetables or above ground protected plants).

                                                      5i               ..         (VI-6)
                                            (P.)

where:
     Pv,       =   concentration of constituent due to air-to-plant transfer in the 1th plant
                   group, mg constituent/kg plant tissue DW
     Cy       =   vapor-phase concentration of constituent in air due to direct emissions,
                   jig constituent/m3 air
     Bv,       =   air-to-plant biotransfer factor for the i* plant group, [mg constituent/kg
                   plant tissue DW]/[mg constituent/kg air]
     VG.g      =   above ground plant correction factor, unitless
     pa         =   density of air, kg/m3
     103       =   units conversion, mg/10Vg

     Parameter values used in the above equation  are presented in Appendix V-7.  These
factors are related to various physical and chemical properties of the constituents.  Equations
recommended by U.S.  EPA (1994c) to  estimate Bv, are also presented  in Appendix V-7.  Cy
is predicted from the air dispersion modeling.  VG^ is a correction factor similar to VG^
that is introduced to reflect the difference between the concentration in the outer few
millimeters and the average concentration in the whole vegetable.  U.S. EPA (1994c)
recommends that VG,g  should be set equal to 0.01 for unspecified above ground fruits and
vegetables, 1.0 for leafy vegetables and forage, and 0.5 for silage and  0 for grain.   These
recommendations are based, in part, on the reduction of chemical concentrations in
unspecified fruits and vegetables as a result of  cleaning and peeling; the direct analogy of
leafy vegetables and forage to azalea leaves, the experimental leaves on jvhich the equation
was based; the assumption that silage can be considered part leafy  and  part protected; and the
assumption that grain is fully protected.  The density of air, related to the site-specific air
temperature, is presented in Table VI-1.

Volume V                                --  •
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 D.   Estimation of Meat, Eggs and Milk Concentrations
      Stack gas constituents in soil, surface water, and plants may accumulate in animals that
 ingest these media while grazing.  The uptake of chemicals  by livestock is required to
 estimate human exposure to constituents that accumulate in milk and meat products from
 animals that are raised in the vicinity of the WTI facility.  U.S.  EPA (1990a;  1994c) presents
 a food chain model to estimate concentrations of stack gas constituents in beef. milk. pork.
 poultry, and eggs,  etc.  This model considers the concentration of constituents in plan's, and
 soil, the quantity of plants, and soil that animals consume, and the biotransfer (Ba) or
 bioconcentration factor (BCF) of each type of animal tissue.  According to U.S. EPA
 (1994c), uptake of constituents via inhalation or ingestion of contaminated water is
 insignificant compared to soil and fodder ingestion and is, therefore, not considered in this
 assessment.
      The algorithm used to estimate constituent concentrations in animal tissues is expressed
 as follows:
                    CB   =

or for dioxin-like compounds1:

               CB  =
                                                                (MF)
                                                          (VI-7)
                         1-1
                                                               (BCF)
                                                          (VI-8)
where:
     CB
     Qp,- or Dfp,    =
concentration of constituent in the "f" animal tissue group, mg
constituent/kg animal tissue fresh weight
quantity of i"1 plant group eaten by the jtt animal each day or
fraction of diet that is 1th plant group, kg plant tissue DW/day or
unitless
total concentration of constituent in the r* plant  group eaten by the
j* animal, mg constituent/kg plant tissue dry weight
fraction of feed  from on-site sources (additional adjustment  factor
to account for grain or silage that is imported from outside areas),
unitless
    1 In this assessment, dioxin-like compounds are assumed to include all the dioxin and
furan congeners considered and the polychlorinate biphenyl compounds.
Volume V
                                          ATT -r
-------
     Qs  or DFs    =   quantity of soil eaten by the j* animal each day or fraction of diet
                        that is soil, kg soil/day or unitless
     CS            =   soil concentration, mg constituent/kg soil
     Bs            =   soil bioavailability term, unitless
     Ba,            =   biotransfer factor for the j* animal tissue group, d/kg
     MF           =   metabolism factor, unitless
     BCF          =   bioconcentration factor for dioxin-like compounds, unitless
     fatj            =   fraction of j* animal tissue that is fat, unitless

     These equations include uptake of chemicals by livestock through ingestion of fodder
and soil.  Appendix V-7 presents the necessary input parameters on the type and amount of
plants and soil consumed by various animals.
     The biotransfer (bioconcentration) factors used in this assessment are derived from  three
sources.  For the dioxin-like compounds, BCFs recommended by U.S. EPA (1994b) are used
(see equation (VI-8)).  For the organic chemicals, regression equations presented by Travis
and Arms (1988) and recommended by U.S. EPA (1993a) relating Ba to K^, are used.  For
metals, Ba values presented by U.S. EPA (1995c), Baes et al. (1984), and other literature
sources are used.
     The regression equation used to estimate biotransfer factors for organic chemicals
developed by Travis and Arms (1988) is based on data for a limited group of compounds
comprised primarily of pesticides and chlorinated compounds. In the HHRA, biotransfer
factors estimated using this regression equation are applied to the non-dioxin organic
compounds.  Sufficient scientific evidence exists (Dceda 1980; Astill 1989; Daniel and Bratt
1974; Albro 1986), however, to indicate that bis(2-ethylhexyl)phthalate is metabolized in the
body of mammals and does  not bioaccumulate to the extent implied by using the Travis and
Arms regression equation.  Therefore, a "metabolism factor", MF, is introduced in equation
(VI-7) to  account for metabolism in beef cattle, milk cows, and humans.  The value of MF  is
estimated to be 0.01 for bis(2-ethylhexyl)phthalate (BEHP) based on a study by Dceda et  al.
(1980).  An analagous MF was applied to di(n)octylphthalate (DNOP) because of the close'
similarity between DNOP and BEHP in chemical structure and metabolism of ester bonds
(DeAngelo et al. 1986).  DNOP and BEHP are chemical isomers and, therefore, will behave
comparably in the environment.  Like BEHP, metabolism of DNOP has been observed in
several species including man  (Lake et al. 1977).  In fact, Kaneshima et al. (1978) reported
that in rats, the  metabolism  rate of DNOP was faster than that of BEHPV, Quantitative data
to calculate an MF for DNOP, however, were  not available from this study or other
literature sources.  Because  of DNOP's similarity to BEHP, an MF equivalent to that for
BEHP was assigned to DNOP. Additional discussion of the metabolism, absorption, and

Volume V                               *™ "
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excretion of BEHP and DNOP is presented in Appendix V-7.  For all other compounds, the
value of MF is conservatively assumed to be 1.0.
     F,  is a site-specific value that has been obtained from discussions with a local
agricultural agent (Miller 1993), as shown in Table VI- 1.  This value equals 0.9 for grain
and silage for  dairy cows and 1.0 for all  else. These values imply that only 10% of a dairy
cattle's grain and silage intake is imported from outside areas with the balance from local
sources.

E.   Estimation of Surface Water Concentrations
     Surface water bodies may receive stack gas constituents from direct deposition, from
runoff of contaminated soils in the vicinity of the WTI facility, and from eroded soils.  The
concentration of constituents in the surface water is required to estimate human exposure
through surface water ingestion and dermal contact, and to estimate the uptake of chemicals
from the surface water by fish.  U.S. EPA (1994c) presents  a model to estimate constituent
concentrations in surface water bodies. This algorithm contains several  simplifying and
conservative assumptions, as  follows:

     •    Soil concentrations within  a watershed are uniform;

     •    Chemicals enter into a surface  water body via soil erosion, surface runoff,  and
          direct deposition; and

     •    Steady-state is achieved between concentrations in the dissolved phase in the water
          column, concentrations in  the suspended sediment, and  concentrations in bottom
          sediments.

     To determine surface water concentrations, the concentration on the suspended sediment
must be estimated.  The suspended sediment concentration is calculated from the total  load  of
constituent to the water body and the annual amount of suspended sediment, as presented in
Appendix V-7 and summarized below:

                                            -                                    CVI-9)
where:
                                                                /•••
     Qsed =   concentration on suspended sediment, mg/kg
     p    =   annual contaminant entry via erosion  + direct deposition, mg/yr
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         =   annual amount of suspended sediment, kg/yr

The values for p and  are determined by the equations in Appendix V-7.
     Once the suspended sediment concentration is determined, the dissolved concentration is
estimated by calculating a mass balance between the mass of contaminants entering the water
body and the amount that partitions to the three compartments in the water body: a) dissolved
in the water column, b) sorbed to suspended material, and c) sorbed to particles settling to
the bottom.  Specifically, the dissolved concentration is estimated by the following equation:

                                     CW   =   Caed                     ..       (VI-10)
where:
     CW      =    dissolved-phase concentration in water column, mg/L
     C5sed      =    concentration on suspended sediment, mg/kg
     Kd,,,^     =    sediment-water partition coefficient for contaminated suspended
                    sediment, L/kg

     The bottom sediment concentration is determined by the following relationship with the
concentration on the suspended sediment estimated by:
where:
     C,^       =   concentration on bottom sediment, mg/kg
     Cittd      =   concentration on suspended  sediment, mg/kg
         ,      =   fraction organic carbon in bottom sediment, unitless
         .A     —   fraction organic carbon in suspended sediment, unitless

     The equations and parameter values used in this assessment are presented in Appendix
V-7.  Site-specific values are needed for several parameters to characterize the water body
and watershed area (e.g., water body surface area, volume, and total suspended  solids, and
watershed area) and are presented in Table VI-1.  These values are obtained from the
literature and are described further in Appendix V-7.  The chemical-specific partition
coefficient, KdHed, is estimated from the organic carbon coefficient, K,,,., and the  fraction of
organic carbon in the suspended  sediments.


Volume V                                -<™ ^
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 F.  Estimation of Chemical Concentrations in Fish
     Stack emissions may enter local surface water bodies through both direct deposition and
 deposition onto waittshed soils, followed by runoff and erosion into the surface water
 bodies.  These chemicals may then accumulate in fish tissue.  The concentration of
 constituents in fish is required to estimate human exposure to constituents via ingestion of
 fish.  U.S. EPA (1990a) presents a model to estimate chemical concentrations in fish.  This
 model, which calculates constituent concentrations  by considering the water concentration and
 a bioconcentration factor,  is generally appropriate for chemicals with high water solubility
 and low affinity for sediments.
     The water concentration and a bioconcentration  factor are necessary to .estimate
 concentrations of constituents in fish, as shown in Appendix V-7 and as follows:

                                  CF  =   C    (BAF)                          (VM2)
where:
     CF       =   concentration in fish, mg/kg
     Cwat       =   dissolved water concentration, mg/L
     BAF      =   bioaccumulation factor, L/kg

     Estimation of water concentrations has been described previously.  BAFs are calculated
as the product of a bioconcentration factor (BCF) and a food-chain multiplier (FCM) (U.S.
EPA 1995d).  U.S. EPA (1995d) presents FCMs for various trophic levels based on the
logarithm of K^.  The FCMs for the piscivorous fish trophic level are used in this
assessment.  BCF values for specific substances of concern are compiled from the scientific
literature and other sources, e.g., die U.S. EPA AQUIRE data base.
     An alternative equation is applied to dioxin-like compounds because of their low water
solubility and high affinity to  sediments (Appendix V-7), as follows:

                             CF  =        -
where:
     C,^       =   bottom sediment total concentration, mg/kg
     OCied     =   fraction organic carbon in bolom sediment, unitless
                                                                /••
     BSAF     =   biota to sediment accumulation factor, unitless
     f^d       =   fraction lipid content of fish, unitless
Volume V                                VT-11
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     Default values are used for OC,^ and f^^ because of the likely variability in site-
specific data; BSAF is chemical-specific, and values recommended by U.S. EPA are used in
this assessment (U.S.  EPA 1994c).  Specific parameter values used in this assessment can be
found in Appendix V-7.

G.  Estimation of Breast Milk Concentrations
     Constituents in breast milk provide an exposure pathway for infants, a potentially
sensitive population subgroup.  For dioxin-like compounds, Smith (1987) has developed an
approach to estimating concentrations in breast milk. This approach is based on the half-life
of dioxins within the human body, estimated as five to seven years (U.S. EPA 1994a). and is
shown as follows:
                               c    =   v 7 v y yv M-M                       (vi-14)
                                mm      (0.693) (A) ^£1)]
where:
     C,,,,,,  =   chemical concentration in mother's milk fat, mg/kg
     m    =   lifetime average maternal intake of dioxin-like compound, mg/kg of body
              weight/day
     h    =   half-life of dioxin in adults, days
     fj    =   proportion of ingested dioxin-like compound stored in fat
     f2    =   proportion of mother's weight that is fat, kg maternal fat/kg total body weight
     LT   =   lifetime,  days
     ED   =   exposure duration, days

The lifetime average maternal intake, m, is the average daily dose the mother receives during
her lifetime, rather than  the dose during the period of exposure.  Therefore, the LT over ED
factor is included to correct for the lifetime averaging used in the estimation of maternal
intake (i.e., to estimate an average  daily dose during the period of exposure).  Parameter
values used in the assessment are shown in Appendix V-7.
     Travis et al. (1988) presents a generic, alternative methodology to estimate breast milk
concentrations for chemicals not amenable to the  Smith (1987) approach (i.e., chemicals
other than dioxins/furans and PCBs). This methodology is summarized in Appendix V-7 and
below:
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                                                 (f )
where:
     C^  =   constituent concentration in mother's milk fat, mg/kg
     Mu  =   maternal total daily intake from all routes of exposure, mg/day
     T?^  =   mother's milk fat biotransfer factor, day/kg
     MF  =   metabolism factor, unitless

     The method used to estimate the mothers' total daily intake is summarized in Appendix
V-7.  Biotransfer factors are a function of K^, and are calculated by the modified Travis et
al. (1988) equation shown in Appendix V-7. As noted earlier, the value for MF is 1.0 for
all chemicals, except for bis(2-ethylhexyl)phthalate for which a value of 0.01 is assigned.
Additional discussion of this approach is presented in Appendix V-7.
     Inorganic compounds,  including metals, are not generally lipophilic and thus
accumulation in mother's milk is not anticipated.

H.   Uncertainties
     Uncertainties in estimating chemical concentrations in the environment are classified as
follows:

     •   Uncertainties inherent in the fate and transport models used to predict
         environmental concentrations; and

     •   Uncertainties in the parameters values used as inputs to the fate and transport
         models.

     These two types of uncertainty are discussed separately below.  A quantitative
evaluation of the effect of uncertainties in the environmental modeling is presented in
Chapter IX.  In addition, Table VI-2 identifies the key assumptions used in estimating
environmental concentrations.  The basis for each assumption  is provided in the table, as
well as the estimated direction and magnitude of effect that the assumption could have on the
results of the HHRA.  As indicated in Table VI-2, several of the assumptions used in this
chapter could significantly impact the results of the assessment,  if these assumptions are
incorrect.  Significant uncertainty is associated with the accuracy of the fate and transport
models because of the simplifying assumptions used in the derivation of these models and the
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limited, largely lab-scale, validation that has been conducted.  As noted earlier, conservative
assumptions are applied in this assessment to account for this uncertainty.
     Chemical-specific input values used in the fate and transport equations may also have a
significant effect on the results of the risk assessment. Specifically, K^ values used in many
of the models are highly uncertain and may have a significant impact on estimated
concentrations in environmental media. In addition, estimates of K^ values for some
chemicals range over several orders of magnitude.

     1.   Uncertainties Inherent in the Fate and Transport Models
         As outlined in this chapter, it is necessary to rely on models to predict chemical
     behavior in the environment following release from the WTI facility.  These models,
     while based on fundamental scientific principles, represent a simplification of the
     processes that will determine actual chemical concentrations in air, soil, surface water,
     and other environmental media. Such  simplification can, in theory, lead to either an
     overestimation or underestimation of chemical concentrations in the various
     environmental media.  In this risk assessment, models are selected that are more  likely
     to overestimate, rather than underestimate,  chemical concentrations in the environment
     given conservative input parameters to these models.
         The models used to predict chemical concentrations in soil,  vegetables,  meat, milk,
     surface water, fish, and breast milk are based primarily on  the scientific principles of:
     1) mass balance,  and 2) chemical partitioning.   Use of mass balance principles ensures
     that the total mass of a contaminant is taken into account, for example, in predicting
     soil concentrations.  Chemical partitioning indicates what fraction of the total mass will
     be transferred from one medium to another and dictates parameters such as biotransfer
     factors  (BTFs) and bioconcentration factors (BCFs).  Uncertainty is associated with both
     mass balance and partitioning model approaches, due to incomplete knowledge in
     several  areas, including the nature, rate, and extent of chemical degradation in the
     environment, the types of chemicals produced by such degradation, and the chemical,
     physical, and biological factors that determine the movement of a chemical from one
     environmental medium to another.
         Specific uncertainties  associated with the fate and transport modeling used for
     dioxin and furan cogeners are discussed below because these groups of compounds are
     likely to be the primary contributor to total cancer risk due  to human exposure to
     incinerator stack emissions. This risk assessment relies on the fate and transport
     modeling described in the U.S. EPA document: Estimating  Exposure to Dioxin-Like
     Compounds: Volume III (U.S. EPA 1994c), which  was recently  reviewed by the U.S.
     EPA's  Science Advisory Board (U.S. EPA  1995e).  The Science Advisory Board's

Volume V                               -— -
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     comments on some of the major fate and transport modeling issues for dioxins and
     furans are summarized below.

     •    The role of combustor emissions  on long-term accumulation of dioxins and furans
          in sediments and soil requires further study.

     •    The existing air dispersion models adequately simulate the atmospheric transport of
          vapor-phase dioxins and furans, but are unable to account for partitioning
          processes onto soil, vegetation, and water surfaces.

     •    The available qualitative evidence suggests that the lesser chlorinated dioxins and
          furan congeners are degraded by  photolysis between the source and environmental
          sinks.   This degradation is not accounted for in the fate and transport modeling.

     •    The primary physical/chemical properties of the individual dioxin and furan
          congeners, other than 2,3,7,8-TCDD, are developed based  on limited data, which
          introduces some uncertainty in the estimates of environmental concentrations.

     •    Validation of the vapor/particle pardoning model (Bidleman 1988) is required over
          the broad temperature range typical of environmental conditions.

          Further details regarding the  Science Advisory Board's comments may be found
     in:  An SAB Report: A Second Look at Dioxin.  Review  of the Office of Research and
     Development's Reassessment of Dioxin and Dioxin-Like  Compounds by the Dioxin
     Reassessment Review Committee (U.S. EPA 1995e).

     2.    Uncertainties in Input Parameters
          The fate and transport models used to predict concentrations in the environment
     require inputs regarding both the environmental media (e.g., soil density, wind speed,
     fraction organic content in soil  and sediment) and the physical/chemical properties of
     the chemicals of concern (e.g., bioconcentration factors, solubility, Henry's Law
     constants).  In some cases, only limited data are available regarding a property of an
     environmental medium or chemical. For example, biotransfer factors  have not been
     directly measured for certain chemicals cons:dered  in this assessment,  and thus are
                                                               «•
     extrapolated using regression equations based on available data for  other chemicals.
     Many of these regression equations are based on the octanol/water  partition coefficient,
        .  The value of Kw for many chemicals is highly uncertain, with estimated values
Volume V
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      for a single chemical potentially ranging several orders of magnitude. Furthermore,
      regression equations are often based on the study of a limited number or specific class
      of compounds (e.g., pesticides). The uncertainty associated with applying these
      regressions to compounds outside the class of compounds used in the original study may
      be significant. These data gaps introduce  uncertainty in the model results.  In other
      cases, there is considerable variability in the available data, and a single value from a
      range or distribution of reported values for a parameter is  selected  for use in the risk
      assessment.
          It is not possible to rigorously quantify the effect of all uncertainties introduced
      into the risk assessment by the fate and transport models and inputs to these models.
      However, a quantitative evaluation of the uncertainties in the fate and transport
      modeling for two types of chemicals of primary concern in the risk assessment (dioxins
      and metals) is performed, and is presented in Chapter DC.
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Table Vl-l
Site-Specific Parameters for Fate and Transport Modeling

ocK,
BD
P
I
RO
Ev
o.
R
Parameter
Fraction of organic carbon in soil
(unitless)
Bulk density of soil (g/cm')
Precipitation (cm/yr)
Irrigation (cm/yr)
Runoff (cm/yr)
Ev*apotranspiration (cm/yr)
Soil volumetric water content (mL/cm3)
USLE erosivity (yr'1)
Value
0.013
1. 31
95
28
25
44
0.25
125
Media
plant,
soil
soil
soil
soil
soil
soil
soil
soil
Basis
average of organic matter values provided in the Soil
Conservation Service soil surveys of Beaver & Lawrence
(USDA SCS 1982), Greene & Washington (USDA SCS 1983),
Butler (USDA SCS 1989), and Allegheny counties, PA (USDA
SCS 1981); Brooke, Hancock, & Ohio counties, WV (USDA
SCS 1974); and Columbiana county, OH (USDA SCS 1968)
and assumption that the organic matter is comprised of 40-50%
carbon (Foth and Turk 1972)
average of values provided in the Soil Conservation Eervice soil
surveys of Beaver & Lawrence (USDA SCS 1982), Greene &
Washington (USDA SCS 1983), and Butler counties, PA
(USDA SCS 1989)
average of values provided in the Soil Conservation Service soil
surveys of Beaver & Lawrence (USDA SCS 1982), Greene &
Washington (USDA SCS 1983), Butler (USDA SCS 1989), and
Allegheny counties, PA (USDA SCS 1981); Brooke, Hancock,
& Ohio counties, WV (USDA SCS 1974); and Columbiana
county, OH (USDA SCS 1968)
PA average (personal communication, Jarrett 1994)
PA average (personal communication, Jarrett 1994)
based on meteorological data from Columbus, OH (personal
communication, Reinke 1994)
regional average (personal communication, Seibert 1994)
constant for Allegheny county, PA (personal communication,
Moyer 1994)
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VI-17
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Table VI-1 (continued)
Site-Specific Parameters for Fate and Transport Modeling

K
u
T
P.
P.
TP
YP
F
Parameter
USLE erodability (tons/acre)
Wind speed (m/sec)
Air temperature (K)
Viscosity of air (g/cm-sec)
Density of air (g/cm1)
Length of exposure to deposition per
harvest of the edible portion (yr)
Standing crop biomass (kg DW/m2)
Fraction of feed from on-site sources
Value
0.34
4.1
283
1.76x 10*
1.25x 10 3
0.226 a-g exposed
0.288 leafy
0.315 forage
0.082 silage
0.09 a-g exposed
0.1 8 leafy
0.449 forage
2.989 silage
0.9 for grain and
silage for dairy
cows, 1.0 for all
else
Media
soil
soil
plant,
soil
soil
soil,
plant
plant
plant
animal
Basis
average of values provided in the Soil Conservation Service soil
surveys of Beaver & Lawrence (USDA SCS 1982), Greene &
Washington (USDA SCS 1983), and Butler counties, PA
(USDA SCS 1989)
based on meteorological data from Pittsburgh, PA (personal
communication, Vreeland 1994)
average of values provided in the Soil Conservation Service soil
surveys of Beaver & Lawrence (USDA SCS 1982), Greene &
Washington (USDA SCS 1983), Butler (USDA SCS 1989), and
Allegheny counties, PA (USDA SCS 1981); Brooke, Hancock,
& Ohio counties, WV (USDA SCS 1974); and Columbiana
county, OH (USDA SCS 1968)
calculated from the air temperature (Munson et al. 1990)
calculated from the air temperature (Munson el al. 1990)
time of harvesting activity (PDA 1994)
literature values for aboveground exposed and leafy vegetable
(Belcher and Travis 1989), average 1987 and 1992 grain,
forage, and silage values. from Census of Agriculture (USDC
1993a, 1993b, 1993c) :
personal communication, Miller 1993
Volume V
VI-18
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Table Vl-l (continued)
Site-Specific Parameters for Fate and Transport Modeling

A,
A^,
v«,
TSS
PER
Parameter
Effective watershed area (m2)
Surface area of water body (m2)
Volume of water (L/yr)
Total suspended solids (mg/L)
Particle emission rate (g/s)
Value
5.57 x 107 (TR L.)
1.3 x 10' (LBC)
4 x 10" (Ohio R.)
1.2 x 105(TRL.)
2.4 x 105 (LBC)
varies by subarea
(Ohio R.)
l.46x 10'°(TRL.)
4.7 x 10" (LBC)
3.4x 10" (OhioR.)
19 (TR L.)
12 (LBC)
20 (Ohio R.)
0.07
0.07
Media
lake
river
lake
river
lake
river
lake
river
lake
river
Basis
CES 1994
USGS 1993
professional judgement
CES 1994
30 m avg width and 8,050 m length (professional judgement)
450 m avg width and lengths of 3.5, 3, 2, 2, 3, and 6.5 river
miles in the E3, E2, El, SI, W2, and W3 subareas,
respectively (professional judgement)
CES 1994
USGS 1993
personal communication, Fraser 1995
avg of bimonthly samples at three locations (CES 1994)
personal communication, Davic 1995
average of 10/89 to 6/92 monthly measurements from East
Liverpool Station, Ohio River (personal communication, Fraser
1995)
average of 33 runs from the trial burns and performance tests
a-g exposed = above ground exposed fruit and vegetables
TR L. = Tomlinson Run Lake
LBC >: = Little Beaver Creek
Ohio R. = Ohio River
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VI-19
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TABLE VI-2
Key Assumptions in Fate and Transport Modeling
Assumption
Fate and transport modeling accurately reflects
reality
Chemical -specific inputs are appropriate
Site-specific inputs are appropriate
The surrounding area is an agricultural watershed
that has a soil mixing zone of 10 cm
The chemicals mix completely within the soil layer
of interest (I, 10, or 20 cm)
The facility operates continuously for 30 years
Volatilization losses do not occur once the chemical
is deposited
Degradation of organic contaminants in soil is first-
order
Basis
The U.S. EPA-recommended (U.S. EPA 1990a,
1993, 1994a) models used in this assessment are based
on the best available data (although somewhat
limited). To account for potential uncertainty
associated with the use of these data, conservative
assumptions are generally applied in developing these
models.
Professional judgment on best available data.
Professional judgment on best available data.
U.S. EPA (I994a) guidance assuming an agricultural
watershed has some tilled and some unfilled soils.
Substances are assumed to remain within the top 10
centimeters of soil; losses due to percolation are not
considered.
U.S. EPA (1990a) guidance assuming tilling in
agricultural lands. Substances are assumed to remain
within the specified soil layer; losses due to
percolation are not considered.
Conservative assumption although it is highly unlikely
that the facility will operate 100% of the time for 30
years. The facility only operated 53% of the time in
the first year.
Conservative assumption based on professional
judgment.
Simplifying assumption to explain a complex process
that is not necessarily first-order.
Magnitude of
Effect
high
high
low
low
low
low
low
low
Direction of Effect
possible
overestimate
unknown
unknown
overestimate
overestimate
likely overestimate
" 1
overestimate
unknown
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TABLE VI-2 (continued)
Key Assumptions in Fate and Transport Modeling
Assumption
Fruits and vegetables are modeled as four types of
vegetable classes
Exposure to contaminants for aboveground protected
vegetables and root vegetables occurs only through
root uptake (i.e., does not occur via direct deposition
and air-to-plant transfer)
Uptake transfer factors for root uptake and air-to-leaf
uptake are based on K^,
Inhalation and surface water ingestion by animals are
not evaluated
Meat biotransfer (Ba) and bioconcentration (BCF)
factors are appropriate
AH chlorinated biphenyl compounds are considered
to be transported in the same manner as the dioxin
and furan congeners
For surface water:
-Soil concentrations within a watershed are uniform
-Steady-state is achieved between concentrations in
the dissolved phase, suspended sediment, and bottom
sediment
Of the total mercury in the water column, 25%
exists in the methyl mercury form
Basis
U.S. EPA (1990a and 1993) guidance.
U.S. EPA (1990a) guidance based on the likelihood
that these classes of vegetation are not exposed to
contaminants on depositing particles or in vapor form.
U.S. EPA (1990a, 1993) guidance.
These pathways are considered insignificant compared
to fodder and soil ingestion (U.S. EPA 1994a) based
on a review of the literature.
U.S. EPA (1990a and 1994a) guidance and review of
available models.
Conservative assumption based on professional
judgment.
U.S. EPA (1994a) guidance.
U.S. EPA (1994c) guidance that concludes that no
more than 25% of the total mercury in the water
column exists in the methyl mercury form and
typically, less than 10% is observed.
Magnitude of
Effect
low
low
medium
low
high
low
low
low
Direction of Effect
unknown
possible
underestimate
unknown
underestimate
unknown
unknown
unknown
overestimate
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                                                  VI-21
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TABLE VI-2 (continued)
Key Assumptions in Fate and Transport Modeling
Assumption
PAHs are
fish
Inorganic
milk
evaluated as if no metabolism occurs in
compounds do not accumulate in mother's
Basis
Conservative assumption since the literature (ATSDR
1993b; Eisler 1987) suggests that PAHs are readily
metabolized in fish.
Inorganic compounds are generally not lipophilic and
would not tend to accumulate in mother's milk.
Magnitude of
Effect
low
low
Direction of Effect
possible
overestimate
underestimate
Moles:
Key Assumptions regarding dispersion and diffusion are summarized in Volume IV.
low = less than a factor of two
medium = a factor of two to ten
high = greater than a factor of ten
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VI-22
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                  VH.  ESTIMATION OF EXPOSURE DOSE
 A.  Introduction
     Estimates of chemical dose developed in the exposure assessment are used to estimate
 the risks to individuals and to the collective population in the vicinity of the WTI facility.
 U.S. EPA guidelines recommend that the presentation of such estimates for individuals and
 populations be made using several descriptors (U.S. EPA 1992a; 1995a). For example, the
 guidelines call for estimating the "high-end" exposure,  which is an estimate of the exposure
 of individuals in the upper end of the exposure distribution of the population.   Conceptually,
 the U.S. EPA guidelines define high-end exposure as within the upper ten percent of the
 exposure  distribution, but not higher than the upper bound of the distribution (i.e., not above
 the expected  highest value in the true exposure distribution of the population).  The
 guidelines also recommend the development of "central tendency" exposure estimates to
 reflect the exposure borne by typical members of the exposed population, i.e., those
 approximately at the median of the exposure distribution.
     In order to estimate the exposure distribution of the population, it is necessary to
 develop sufficient data to characterize the exposed population.  The method used in this
 assessment to estimate the exposure distribution for the population is based on dividing the
 population into subgroups (identified in Chapter V) made up of individuals expected  to share
 the same exposure characteristics.  These subgroups can be characterized by developing an
 exposure distribution using site-specific information concerning:

     •    The location of the exposure subgroups with  respect to the WTT facility;
     •    Typical activity patterns that generally characterize each subgroup; and
     •    The number of individuals that comprise each subgroup.

     To fully develop an exposure distribution for a subgroup requires detailed information
 concerning the activity and behavioral patterns of individuals in the subgroup,  including the
percent of time spent in performing different activities at designated locations (e.g., indoors,
 outdoors,  garden, school), dietary intake estimates, sources of different food groups within
 the area, age  and  sex of individuals in the population, and other data characterizing human
behavior of the population. For example, it is important to understand the extent to  which
food consumed locally is derived from local sources rather than imported from  more distant
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 sources.  This aspect is particularly important in assessing the fraction of consumed food that
 may be affected by emissions from the WTI incinerator.
     It is recognized that gaps in this information exist, and that some of the activity and
 behavioral patterns will change over time.  However, this methodology should provide a
 reasonable estimate of the exposure distribution within each subgroup.  After distributions
 have been developed for each subgroup,  they can be combined to approximate the exposure
 distribution for the population as a whole.
     The Peer Review Panel emphasized the importance of obtaining site-specific data,
 including information on the amount of consumed meat derived from local  sources, the
 amount of fish derived locally, and the amount of food consumed from local-home gardens.
 As described in the Project Plan (U.S. EPA 1993b), surveys have been conducted to obtain
 site-specific data of this nature.  The data collected  from these efforts, as well as subsequent
 data collected, are described in this chapter.

 B.   Estimation of Human Exposure
     The fate and transport models described in the preceding chapter provide a means of
 estimating environmental media concentrations of substances released from  the WTI facility.
 Exposure to these substances by individuals living and  working in the vicinity of the facility
 may occur as a result of contact (e.g.,  inhalation, ingestion,  dermal contact) with
 contaminated media.  To quantify the magnitude of  this exposure, environmental media
 concentrations are combined with exposure factors in exposure dose equations using the
 methodology described below.

     1.   Estimation of Exposure Dose
          Exposure to a chemical by an individual may occur by either intake, where the
     chemical enters the body through  a body opening  (e.g., the mouth), or uptake, where
     the  chemical is absorbed through a body boundary (e.g., the skin). Exposures through
     both intake and uptake  are of interest in the risk assessment.
          Theoretically, the  dose may be measured  at any one of several locations between
     the point of contact and the location in the body where  the chemical takes effect. It is
     general practice to estimate either the dose at the point of entry into the body (referred
     to as the potential dose), or the dose that has been absorbed through a body boundary
     and is available for biological action (referred to as the internal dose),  depending on the
     exposure route being assessed (U.S. EPA 1992a). In addition, the dose is estimated as
     an average dose  rate  over time.
          When considering intake processes (e.g.,  ingestion, inhalation), the potential dose
     rate is estimated.  For the evaluation of noncancer health  effects, this dose rate is

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      referred to as the average daily potential dose (ADDpoJ and is averaged over the
      exposure duration. In evaluating cancer risks, the daily potential dose is averaged over
      the individual's lifetime and is referred to as the lifetime average daily potential dose
      (LADDpo,).  For uptake processes, where the chemical crosses a body boundary, such as
      the skin,  the internal  dose rate is of interest.  In this case, the average daily internal
      dose (ADDmt) and the lifetime average daily internal dose (LADDmt) are estimated when
      assessing noncancer and cancer health effects, respectively.  Although it is theoretically
      possible to estimate an internal dose for intake processes, such as ingestion  and
      inhalation, by using factors that account for the transfer of chemicals across internal
      boundaries (e.g., lungs, stomach), the chemical-specific data are seldom available to
      perform such an assessment reliably.
           The rate of chemical intake and/or uptake is dependent upon the concentration of
      chemicals in environmental media to which individuals come into contact, and the
      nature and duration of contact. The concentration of chemicals in environmental media
      is estimated using fate and transport models (as described in Chapter VI). The nature
      and duration of contact  with contaminated media is estimated for generally homogenous
      subgroups within the population, based on assumptions about behavior. As
      recommended in U.S. EPA guidelines (U.S. EPA 1992b), these assumptions of
      behavior can be represented by discrete values. These discrete values, referred to as
      exposure factors, represent such parameters as the exposure duration, exposure
      frequency, and the media intake rate.
          The exposure factors are  combined with the media concentrations in equations that
      estimate the ADD or the LADD.  These equations, used to estimate the dose (potential
      or internal), are dependent on the route of exposure  (e.g., ingestion, inhalation, dermal
      contact with water).  In  the following sections, the equation used to estimate the dose
     for each route of exposure is presented.  The input parameters for these equations, i.e.,
     exposure factors, are presented and described in Appendix V-8.

          a.    Inhalation of Air
               When assessing the potential for non-cancer effects, inhalation exposure to
          chemicals in air is calculated using the following equation:

                            ADD   -  (CA)(1R)(ET)(EF)(ED)
                                ""'          (BW)(AT)

          where:
                        =  average daily potential dose, mg/kg-day
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               CA      =   concentration of chemical in air, mg/m3
               IR       =   inhalation rate, nrVhr
               ET       =   exposure time, hr/day
               EF       =   exposure frequency, days/year
               ED      =   exposure duration, years
               BW      =   body weight, kilograms
               AT      =   time over which the dose is averaged, days

               For non-cancer effects, AT is set equal to ED.  In evaluating carcinogenic
          health effects, the LADDp,,, is estimated using the equation abover.but with the AT
          replaced by the number of days in a lifetime, LT.

          b.    Soil Ingestion
               For non-cancer health effects, exposure through incidental soil ingestion is
          calculated using the following equation:
                                                                             (vn.2)
                          ADD   =
                                            (BW)(AT)

         where:
                    ,   =   average daily potential dose, mg/kg-day
              CS       =   chemical concentration in soil, mg/kg
              DR.       =   soil ingestion rate, mg/day
              EF       =   exposure frequency, days/year
              ED       =   exposure duration, years
              BW       =   body  weight, kilograms
              AT       =   time over which the dose is averaged, days

              In assessing non-cancer effects, AT is set equal to ED.  When evaluating
         carcinogenic health effects, the LADD^ is estimated using the equation above, but
         with AT replaced by the number of days in a lifetime, LT.

         c.   Dermal Contact with Soil
              When assessing non-cancer health effects, dermal exposure to chemicals in
         soil is estimated using the  following equation:
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                     ADD   = _   mg  I
                                            (BW)(AT)
                                                                             (Vn-3)
          where:
               ADDmt   =   average daily internal dose, mg/kg-day
               CS       =   chemical concentration in soil, mg/kg
               SA       =   skin surface area available for contact, cm2
               AF       =   soil to skin adherence factor,  mg/cm2-day
               ABS     =   absorption factor, unitless
               EF       =   exposure frequency, days/year
               ED       =   exposure duration, years
               BW      =   body weight, kilograms
               AT       =   time over which the dose is averaged, days

               In assessing non-cancer effects, AT is set equal to ED.  For carcinogenic
          health effects, the LADDmt is estimated using the equation above, but with AT
          replaced by the number of days in a lifetime, LT.

          d.    Ingestion of Locally Raised Beef or Other Meat
               Exposure to chemicals in beef or other meat (or eggs) may occur when
          individuals consume meat products from locally raised livestock or when
          individuals consume meat from locally hunted deer. When assessing potential non-
          cancer health effects, exposure to chemicals in meat products is calculated using
          the following equation:
                                                 (FI)(EF)(ED)
                       ADD   = - V — 8 — I -
                            **             (BW)(AT)

         where:
                        =   average daily potential dose, mg/kg-day
              CB       =   chemical concentration in meat, mg/kg
              IR        =   ingestion rate, g/day
              FI        =   fraction of meat ingested from contaminated source,
                            unitless
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              EF       =   exposure frequency, days/year
              ED       =   exposure duration, years
              BW      =   body weight, kilograms
              AT       =   time over which the dose is averaged, days

              In evaluating non-cancer effects, AT is set equal to ED.  For carcinogenic
          health effects, the LADD^ is estimated using the equation above, but with AT
          replaced by the number of days in a lifetime, LT.

          e.   Ingestion of Milk and Milk Products from Locally Raised Cows
              Exposure to milk and milk products from locally raised cows is calculated for
          chemicals with noncancer health  effects using the following equation:
                                                                             (vn-5)
                       ADD.
                            *"              (BW)(AT)

         where:
                    ,    =   average daily potential dose, mg/kg-day
              CM      =   chemical concentration in milk and milk products on a whole
                            milk basis, mg/kg
              IR        =   ingestion rate, g/day
              FI        =   fraction of milk or milk-product from contaminated source,
                            unitless
              EF       =   exposure frequency, days/year
              ED       =   exposure duration, years
              BW      =   body weight, kilograms
              AT       =   time over which the dose is averaged, days

              In assessing non-cancer risks, AT is set equal to ED.  For carcinogenic
         health effects, the LADD^ is estimated using the equation above, but with AT
         replaced by the number of days in a lifetime, LT.

         f.    Ingestion of Locally Grown Produce
              When evaluating non-cancer effects, exposure to chemicals in locally grown
         produce is calculated using  the following equation:
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                                           l^-^\(FI)(EF)(ED)               (vri-6)
                        ADD   = 	^—^—'-	
                             >*             (BW)(AT)

          where:
                        =   average daily potential dose, mg/kg-day
               CV       =   chemical concentration in vegetables, mg/kg
               IR       =   ingestion rate, g/day
               FI       =   fraction of vegetable diet that is locally grown, unitless
               EF       =   exposure frequency, days/year
               ED       =   exposure duration, years
               BW       =   body weight, kilograms
               AT       =   time over which the dose is averaged, days

               For non-cancer health effects, AT is set equal to ED.  For carcinogenic
          health effects, the LADD^, is estimated using the equation above,  but with AT
          replaced by the number of days in a lifetime, LT.  It should be noted that FI may
          be zero for vegetables not grown in the study area when assessing individual risk.

          g.    Ingestion of Surface Water
               In assessing  non-cancer health effects, exposure to chemicals  in surface water
          is calculated using the following equation:

                           ADD    -  (CW)(IK)(ET)(EF)(ED)
                               *"         (BW)(AT)

          where:
              ADD,*,,   =   average daily potential dose, mg/kg-day
              CW      =   chemical concentration in surface water, mg/L
              IR       =   ingestion rate, L/hr
              ET      =   exposure time, hours/day
              EF      =   exposure frequency, days/year
              ED      =   exposure duration,  years
              BW      =   body weight, kilograms
                                                               »••••
              AT      =   time over which the dose is averaged, days
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               For non-cancer health effects, AT is set equal to ED.  For carcinogenic
          health effects, the LADD^, is estimated using the equation above, but with AT
          replaced by the number of days in a lifetime, LT.

          h.   Dermal Contact with Surface Water
               In assessing non-cancer health effects, dermal exposure to chemicals in
          surface water is estimated using the following equation:
                                    _
                                 "*         (BW)(AT)

          where:
               ADDmt   =   average daily internal dose, mg/kg-day
               DAjv^t   =   adsorbed dose per event, mg/cm2-event
               SA       =   skin surface area available for contact, cm2
               EF       =   exposure frequency, events/year
               ED       =   exposure duration, years
               BW      =   body weight,  kilograms
               AT       =   time over which the dose is averaged, days

               For non-cancer health effects AT is set equal to ED.  For carcinogenic health
          effects, the LADDmt is estimated using the equation above, but with AT replaced
          by the number of days in a lifetime, LT.  DA^^ is estimated in accordance to
          U.S. EPA guidance (U.S. EPA 1992c), as described in Appendix V-8.

          i.    Ingestion of Locally Caught Fish
               When assessing non-cancer health effects exposure to chemicals in fish caught
          in local surface water bodies is calculated using the following equation:
                                                                              (vn.9)
                        ADD   =  -
                            *"              (BW)(AT)
         where:
              ADDpol   =    average daily potential dose, mg/kg-day
              CF       =    chemical concentration in fish, mg/kg
              IR        =    ingestion rate, g/day
              FI        =    fraction of fish ingested that are caught locally, unitless
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               EF       =   exposure frequency, days/year
               ED       =   exposure duration, years
               B"W       =   body weight, kilograms
               AT       =   time over which the dose is averaged, days

               For non-cancer health effects, AT is set equal to ED. For carcinogenic
          health effects, the LADD,^ is estimated using the equation above, but with AT
          replaced by the number of days in a lifetime, LT.

          j.    Ingestion of Breast Milk
               When assessing non-cancer health effects,  exposure to chemicals in breast
          milk is calculated using the following equation:
                                                      -                       (vn-io)
                          LADD    =
                                             (BW)(LT)

          where:
                        =   lifetime average daily dose, mg/kg-day
               C^      =   chemical  concentration in mother's milk, mg/kg
               f4        =   fraction of ingested contaminant that is absorbed, unitless
               IR       =   ingestion  rate,  g/day
               ED       =   exposure  duration, days
               BW      =   body weight, kilograms
               LT       =   lifetime, days

               Noncarcinogenic health effects due to infant ingestion  of breast milk are not
          considered in this assessment due to the significant uncertainty in applying health
          effects/toxicity data to infants  (U.S. EPA 1994a).

     2.    Exposure Factors
          The dose equations identified in the preceding sections include various exposure
     factors, such as contact rate,  and exposure frequency and duration.  Each of these
     factors has a range of possible values based on the popuktion subgroup and exposure
     pathway of interest. Estimation of  typical exposures for each subgroup is performed by
     combining exposure factors reflecting typical activity and behavior patterns of the
     subgroup with media concentrations to which the subgroups may be exposed. Typical


Volume V                              ITTT n
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     values for the exposure factors used in the various dose equations listed above are
     presented in Appendix V-8.  The high-end of the population exposure distribution
     includes highly exposed subgroups from areas most significantly impacted by  the
     facility.  A further assessment of the variability of exposure to these individuals is
     described in Chapter Vm by applying a combination of typical and high-end exposure
     factor values,  as recommended by U.S. EPA (1992b) guidelines.  A summary of typical
     and high-end exposure factor values is presented in Appendix V-8.
          In Appendix V-8, typical values refer to values that represent either the mean  or
     the median of the distribution of possible values.  As noted in the Exposure Assessment
     Guidelines (U.S. EPA 1992b), for skewed or truncated distributions, the median may be
     more representative of the central tendency value than the mean.  Most exposure factor
     distributions are skewed or truncated; therefore, when possible, the median value is
     used in the HHRA. High-end represents the values toward the upper end of the
     distribution, generally 90th percentile and greater.
          As described in Appendix V-8,  site-specific information and U.S. EPA guidance
     (U.S. EPA 1989b; 1990b; 1992c) are generally  relied upon in estimating appropriate
     values for the  exposure factors.   In some instances, professional judgment is applied in
     the selection of exposure factor values. A discussion of the site-specific data relied
     upon in developing exposure factors is provided in the following sections.  Assumptions
     based on U.S. EPA guidance or professional judgment used in developing exposure
     factors are discussed in Appendix V-8.

C.   Site-Specific Exposure Data
     In order to provide a more complete understanding of the exposure to the population
surrounding the WTI facility, site-specific  data characterizing this population, land use
characteristics, local topography, and the local meteorology are used wherever possible in the
risk assessment.  These site-specific data are used in the risk assessment to estimate the
potential exposure to the actual population living or working in the area surrounding the WTI
incinerator.  Table VII-1  summarizes the exposure factors used in the exposure dose
equations for which site-specific data are available.

     1.   Home Gardening Practices
          An informal home gardening survey was conducted in June 1993 by the East
     Liverpool Board of Health in six sections of East Liverpool:  1) East End (half a mile
     northeast of WTI); 2)  Dixonville (half a mile north of WTI); 3) Northside (2 miles
     northwest of WTI); 4) LaCroft (3 miles northwest of WTI); 5) Pleasant Heights
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     (2 miles west of WTI); and 6) Downtown (2 miles southwest of WTI). This survey
     indicated that approximately 30 percent of .local residents have home gardens.  Of the
     residents with home gardens, the Board of Health contacted  100 residents, to ascertain
     gardening practices, such as the types of vegetables and fruit grown and percentage of
     their total vegetable/fruit intake that is homegrown. The data from the home gardening
     survey provide a general indication of gardening practices in the East Liverpool area.
     and are tabulated in Tables  VH-2 and VH-3.  These tables include the  general locations
     of vegetable gardens in the  East Liverpool area,  the vegetables and fruit grown in home
     gardens, and the estimated portion of vegetable and fruit diet that is homegrown.  The
     information on home gardening practices collected by the Board of Health is used to
     estimate the fraction of homes in the area surrounding WTI that have gardens and the
     fraction  of residents' fruit and vegetable diets that are  homegrown, as  indicated in Table
     vn-i.

     2.    Local Fishing Practices
          Fishing practices  in the Ohio River valley in the vicinity of the WTI facility were
     evaluated by the Ohio  and West Virginia Departments of Natural Resources (DNR) in a
     joint recreational fishing study (ODNR 1994a) conducted to identify the amount of
     fishing and the types of fish being caught along the Ohio River between the
     Ohio/Pennsylvania  border (Ohio River Mile 40.1) and Greenup Dam, 300 miles
     downstream (ORM 341).  This 300-mile study area was subdivided into 32 survey
     areas, which include survey points (embayments  and tailwaters), and pools.  Four of the
     32  survey areas (locations #1 to #4) are in the general vicinity (30-kilometer radius) of
     the WTI facility (located at  ORM 41.5).  These four survey areas  were assumed to be
     representative of the Ohio River in the vicinity of the WTI facility.  The four survey
     areas cover the entire stretch of the Ohio River from the Ohio/Pennsylvania border to
     Steubenville, Ohio  (ORM 40.1 to ORM 69.5).
          The DNR study was conducted between April and November 1992.  The amount
     of fishing that occurs between December and March is believed to be insignificant in
     comparison with other parts of the year and should not appreciably affect  the results of
     this survey.  Therefore, the data collected in this study are assumed to reflect annual
     data.  Table VH-4 summarizes the recreational fishing data obtained from  the
     Ohio/West Virginia DNR study (ODNR 1994a).
          The Ohio River Valley Sanitation Commission (ORSANCO) conducted an
     electrofishing survey (between ORM 21.6 and  ORM 55.5) from 1991 to 1993
     (ORSANCO 1994)  that provides the average weight of fish from the Ohio River
     corresponding to various size ranges.  In addition,  ORSANCO performed fish tissue

Volume  V                               ^m 11
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     sampling from 1987 through 1992 at various locations in the Ohio River valley.  The
     resulting data include moisture and lipid content, length and weight information, and
     pesticide,  PCB, and metals concentration in fish tissue (ORSANCO 1988: 1990: 1993).
     As described in the analysis of the fishing data in Appendix V-6. the recreational
     fishing data do not suggest that locally caught fish are a significant portion of the fish
     diet for typical local residents.  Furthermore, the data discussed above are not sufficient
     to indicate the presence or absence of subsistence fishing in the Ohio River Valley area.
     Nonetheless, subsistence fishing is evaluated using exposure factors developed from
     national statistics,  as described in Appendix V-6.

     3.   Local Farming Practices
          Information concerning local farming practices has been obtained from interviews
     with local Agricultural Extension agents who are familiar with farming practices in this
     area  of Ohio,  Pennsylvania, and West Virginia.  In addition, data on local beef farming
     and cattle raising practices were compiled from Agricultural Statistics Service
     (associated with the Departments of Agriculture in Ohio, Pennsylvania, and West
     Virginia) reports and from federal Department of Agriculture reports.  The following
     sections summarize the site-specific data collected on  beef and dairy fanning  practices
     in the area surrounding the WTI facility.

          a.    Beef Fanning
               The primary source of information on beef farming statistics is  agricultural
          data compiled by the Agricultural Statistics Service associated with the
          Departments of Agriculture in each of the three states (Ohio,  Pennsylvania, West
          Virginia) located in the vicinity of WTI (ODA 1994; PDA  1994;  WVDA 1994).
          Summaries of livestock data are published annually and include such parameters
          as: total number of cattle/calves in the  state, number of calves born annually, and
          information on slaughter and marketing of beef cattle and calves.
               A summary of beef farming data for Ohio,  Pennsylvania, and West Virginia
          is provided in Table Vn-5. The value  for total cattle/calves in Table Vn-5 is the
          number of cattle related to beef and dairy farming that were reported in the state
          as of January 1, 1993.   This value includes all types of cattle including: milk
          cows; beef cows used in calving operations; milk and  beef heifers (i.e.,
          replacement cows); steers; bulls; and calves.
               Information on the disposition of beef cattle and calves is also provided in the
          Agricultural Statistics Service summaries.  The number of cattle and calves that
          are slaughtered in registered slaughtering facilities in each state is shown in
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                      Table VH-5.  The source of the slaughtered animals, however, is not available
                      because processing facilities are not required to keep records on  the origin/owner
                      of the cattle sold for slaughter.  A report on the state of the slaughtering industry
                      in Ohio (Distad 1992) indicates that Ohio does not have any "large" capacity cattle
                      slaughtering facilities, but does have many smaller operations with slaughtering
                      capacities of less than 1,000 head per year.  Furthermore, the report indicates that
                      Ohio is a net exporter of beef for slaughter, as indicated by the greater number of
                      steers in the state than head slaughtered (i.e., 229,000 head to  185,000
                      slaughtered).  The same situation would appear to apply in West  Virginia.
                           Pennsylvania, on the other hand, is home to two of the largest cattle
                      slaughtering facilities in the country (10th and 12th largest overall) with  a total
                      annual slaughtering capacity of approximately 740,000 head (Distad 1992): a large
                      fraction of the 740,000 head are likely to be  imported from out of state.   Because
                      of these two very large plants (both of which are located in the eastern part of the
                      state) Pennsylvania is a net importer of beef cattle for slaughter.  For the purpose
                      of this assessment, it is necessary to estimate the number of cattle that are raised
                      as well as slaughtered in Pennsylvania.  Including the data from these importing
                      plants would significantly overestimate the number of locally raised, locally
                      slaughtered cattle.  To obtain an estimate of Pennsylvania-bred cattle slaughtered
                      in the state, therefore, the 740,000 head slaughtered at the large slaughtering
                      houses in eastern Pennsylvania are subtracted from the state total  slaughter.  The
                      resulting estimate,  229,000 head,  is more consistent with the other states  in the
                      area and with the 220,000 beef steers raised in the state (see Table VH-5). This
                      value, therefore, is assumed to approximate the number of Pennsylvania-bred cattle
                      slaughtered in the state.
                          County-specific beef fanning data available from the  Agricultural Statistics
                      Service data summaries  are limited.  Therefore,  a number of parameters are
                      estimated based on state-wide data, as shown  in Table Vn-6. This methodology
                      assumes that beef raising and slaughter practices are  similar across all parts of a
                      state, which may not necessarily be true.  To address this uncertainty, agricultural
                      extension agents for the counties located in the vicinity of the WTI facility were
                      interviewed regarding local beef cattle raising practices.  Although no actual data
                      were obtained from these sources, judgments  concerning local farming practices
/-                    proved to be a  valuable resource to supplement the state-wide data.
V.. -                      For example,  the primary type of beef fanning performed in the eastern
                      Ohio/western Pennsylvania area involves cow/calf operations that  raise cows to
                      produce calves.  These calves are  raised locally for six to nine months, weaned.

            Volume V
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           and generally sold to feedlots out of state (personal communication, county
           agricultural extension agents,  August 1994).  In other portions of these states
           (Ohio, Pennsylvania, West Virginia), this practice may not be as commonplace.
               As a result of the regional variances, the state-wide statistics,  therefore, may
           not accurately represent local beef fanning practices. For example, according  to
           the state-wide data, the fraction of calves born that are  marketed ranges from 0.23
           for Ohio to 0.51 for West Virginia (as shown in Table VEL-5).  Discussions with
           local agricultural extension agents indicate, however, that 60 to 70  percent of a
           local calf crop in any given year is marketed (sold at auction to feedlots in western
           Ohio or the western U.S.) and may range as high as 80 to 90 percent of the local
           calf crop, but is rarely below  50 percent. Because most calves are sent out of  the
           area for slaughter, it is likely  that estimates of local slaughter provided in
           Table VTI-6, overestimate actual local slaughter in these counties.  The published
           and estimated beef statistics for three counties in the vicinity of the WTI facility
          are provided in Table VTJ-6 for the following counties:  Columbiana, Ohio; Beaver.
          Pennsylvania; and Hancock, West Virginia (ODA 1994; PDA 1994; WVDA
           1994).
               A limited amount of data are also available from a 1992 survey of beef cattle
          farms performed by the Beaver Valley Nuclear Power Station located in
          Shippingport, Pennsylvania, approximately 10 miles east of the WTI facility  (PCI
          1992).  Data were collected over a 5-mile radius centered at the power  station.
          The survey indicates that within five miles of the Beaver Valley Power  Station  at
          the time of the survey, there were 67 farms with a total of 909 beef cattle, as
          indicated in  Table Vn-7.   These data are presented  in Figure VTI-1.
               Based on the site-specific data  obtained, it is estimated  that the residents in
          the vicinity of WTI  obtain 15 percent of their beef diet from locally raised
          livestock. Site-specific data are also used to develop estimates of the fraction of
          residents' pork and egg diet  that is from locally raised livestock, as  described in
          Appendix V-8.

          b.   Dairy Fanning
               The number of milk cows, milk production, and milk marketing data
          available from the Agricultural Statistics Services for Ohio, Pennsylvania,  and
          West Virginia (ODA 1994; PDA 1994; WVDA 1994) are summarized in Table
          VTI-8.  To augment these data, agricultural extension agents  representing counties
          in the vicinity of the WTI facility were contacted to provide  a local
          characterization of dairy farming practices (personal communication, county
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          agricultural extension agents, August 1994).  In general, the extension agents
          reported that dairy farming in the eastern Ohio/western Pennsylvania area is not
          significantly different from other parts of Ohio and Pennsylvania, and that state-
          wide statistics are likely applicable to the area around the WTI facility.  Table
          Vn-9 provides estimates of county-specific milk cow herd size and milk
          production statistics, and estimates of milk marketing, based on the state- wide data
          for three counties in the vicinity of the WTI facility.  The milk marketing data
          include information on milk consumption on the farm, marketing to plants/dealers.
          and direct sales to consumers.
               With respect to the milk marketing  data,  it should be noted that Ohio and
          West Virginia do not differentiate between milk sold to plants/dealers and milk
          sold directly to the consumer. The distribution between these  two options shown
          in the Pennsylvania data, therefore, is applied  to the Ohio and West Virginia data.
          This estimate was carried through to the  estimates of county-level milk marketing.
          It is estimated that this assumption does not significantly affect estimates of total
          local milk available in Ohio and West Virginia.  Based on the  data obtained from
          the Agricultural Statistics Services, an estimate of the fraction  of milk consumption
          that is from local sources is  derived.   A value of 36 percent is estimated as
          described in Appendix V-9.
               As noted with the beef farming  data, limited dairy farming data are also
          available from a survey  of dairy farms performed by the Beaver Valley Nuclear
          Power Station.  Data were collected over a 5-mile radius centered at the power
          station and are  summarized in Table  VH-10. The survey indicates that within five
          miles of the Beaver Valley Power Station at the time of the survey, there were 332
          dairy cows,  of which 242 were milked.  The total daily milk production for the
          area is 970 gallons (4.0  gallons/cow).  Although these data are not used to
          estimate local milk consumption, a plot of the locations of these farms, shown in
          Figure VTI-1, indicates that several large  dairy farms are located in  the vicinity of
          the WTI facility (Figure VII- 1 indicates the boundaries of the risk assessment
          study area developed in  Section D of this chapter).
               General locations of dairy farms in the area surrounding the WTI facility are
          based on information from the Agricultural Marketing Service  of the USDA
          (personal communication, J.  Rourke  1994). These data provide information on the
          number  and size of dairy farms per ZIP code area in each of the counties
          surrounding the WTI facility for a single  month, May 1994*  The data for the
          three counties surrounding the facility are tabulated in Appendix V-10 and
          summarized in Table VH-ll.  Figure vn-2 shows the number  of dairy farms by
Volume V
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          ZIP code for several counties in the area of the WTI facility. Although these data
          provide useful information concerning the location of dairy farms in the vicinity of
          WTI, annual data (Table VH-9) are used to develop estimates of local milk
          production because production rates can vary considerably throughout the year.
               It should be noted that Figure VII-2, developed from the May 1994 data.
          shows that many of the farms in Columbiana County are located in the northwest
          portion of the county and very few farms are located in the area immediately
          surrounding  the facility. This information indicates that using county-wide data
          and assuming that dairy farms are equally distributed across the county
          overestimates risk (i.e., production of milk in the area that might-be impacted by
          the facility is lower than assumed).

     4.   Deer Hunting
          The Departments of Natural Resources in Ohio, Pennsylvania, and West Virginia
     were contacted for information on deer hunting in the area surrounding the WTI facility
     (personal communication, ODNR 1994b; PDNR 1994; WVDNR 1995). These agencies
     provided data as summarized in Table VII-12. In addition, these agencies  provided data
     on the number of  hunting licenses issued in Ohio, Pennsylvania, and West  Virginia
     counties, also summarized in Table 33  in Appendix V-8. These data are used to
     estimate typical deer meat consumption rates for deer hunters, as described in Appendix
     V-8.

     5.   Population Data
          Population data for the three-county (Columbiana, Ohio; Beaver, Pennsylvania;
     Hancock, West Virginia) area surrounding the WTI facility are compiled from a
     summary of the 1990 census  developed  by CACI Marketing, Inc. (CACI 1992), as
     shown in Table Vn-13. In addition, the county farming populations are estimated based
     on the number of farms (USDC 1993a,b,c) and the typical household size (CACI 1992)
     in each county.

D.   Development of the Risk Assessment  Study Area and Subareas
     In this risk assessment, population risk, generally defined as the cancer risk burden
across  all exposed individuals, is also evaluated. To facilitate the estimation of population
risks, exposure (and subsequently risks) is estimated for subgroups located in defined
subareas surrounding the WTI facility.   These subareas are developed in order to account for
differences in exposure  at different distances and directions from the facility. Because risk
generally decreases with distance from the facility, a point is eventually reached  where

Volume V                              "-" - '
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inclusion of additional individuals does not significantly affect total population risk (due to
the insignificant increment in exposure of these individuals).  The area within which the
population risk is estimated is referred to as the risk assessment study area.  Outside this
area, risks are anticipated to be relatively insignificant.  The methods used to develop the
risk assessment study area and the subareas within the study area are described below,
followed by an estimation of exposure in the subareas.

     1.   Development of the Risk Assessment Study Area
          The area within which  exposure (and risk) are estimated is referred to as  the risk
     assessment study area. The study area is defined so as to include all individuals  that
     may significantly contribute  to the risk burden of the population in the vicinity of the
     WTI facility.  To ensure that all such individuals are included, the perimeter of the
     study area is defined based on the risk to the  most highly exposed subgroup within the
     exposed population.  Specifically, in this assessment, the study area is initially defined
     based on an estimation of the human health risks associated with the accumulation of
     chlorinated dioxin and furan compounds in locally raised beef, and subsequent  ingestion
     by a subsistence farmer.  This exposure pathway and population subgroup were
     identified in screening-level assessments performed by U.S. EPA as potentially the most
     significant for the WTI facility (U.S. EPA 1993d, 1994g). Furthermore, the perimeter
     of the study area is defined to include locations where excess  cancer risks to a
     subsistence farmer due to beef ingestion are estimated to exceed one in ten  million (1 x
     107).  This level of risk was selected because risks less than 1 x 10* have typically
     been considered  not to be subject to regulatory action by U.S. EPA.  An individual risk
     level below 1 x 10"7 would not likely contribute significantly to the overall risk burden
     of the exposed population living closer to the  facility.
          To understand the relationship between the concentration/deposition predictions of
     the air dispersion modeling and the estimated  risks  of dioxins, a preliminary analysis of
     dioxin/furan cancer risk to a subsistence farmer was conducted. In the preliminary
     analysis,  the location of maximum impact of emissions from the WTI facility (indirect
     and direct cancer risks should be greatest at this location) was used for this purpose.
     Based on the air dispersion/deposition modeling conducted for the risk assessment, the
     location of maximum impact is predicted to be approximately  one kilometer east of the
     WTI facility stack (as indicated in Volume IV). Based on the assumption that a
     subsistence farm could be placed at this location, concentrations of dioxin/furan
     congeners in beef were then  calculated.  These calculations were based  on the fate and
     transport models described in Chapter VI.  Dioxin/furan cancer risks were subsequently
Volume V                               vn.17
-------
     estimated by combining the exposure dose 'vith toxicity values (Table ffl-1) for the
     individual dioxin/furan congeners.
          As a result of this study area analysis, it was noted that plant uptake of vapor-
     phase dioxin/furans is the primary contributor to total risk.  By comparison, uptake of
     dioxins/furans via particle deposition is relatively minor. For example, at the location
     of maximum impact, the contribution of vapor-phase dioxins/furans to the total  risk is
     approximately two orders of magnitude greater than the contribution of either dry or
     wet deposition (see Chapter VIE).  Therefore, the predicted vapor concentrations of
     dioxins/furans are used as a surrogate measure of total risk in this assessment.
          The dioxin/furan cancer risk at the location of maximum vapor impact was
     estimated in the study area analysis to be approximately 2 x 10^ (for beef ingestion by a
     subsistence farmer).  At the point of maximum impact, the air dispersion modeling
     predicts a vapor impact of 0.91 j*g/m3 per gram/second emission rate from the stack
     (i.e., the vapor impact of 0.91 /xg/m3 per  gram/second corresponds approximately to a
     total dioxin/furan cancer risk of 2 x 10^).  The perimeter of the study area used in this
     risk assessment is defined to correspond to a total dioxin/furan cancer risk of 1  x Ifr7. a
     factor of 20 times lower than the estimated risk at  the point of maximum impact.
     Therefore, the perimeter of the study area corresponds to a vapor impact of 0.046
     /zg/m3 (0.91 fj.g/m3 per gram/second divided by 20), which is rounded to 0.05 ftg/m3.
     A plot of the vapor dispersion isopleths (shown in  Appendix IV-1) predicted from the
     air dispersion modeling indicates  that the 0.05 ^g/m3 isopleth is irregular in shape but is
     generally contained within a radius of 12 kilometers (km) of the site. The risk
     assessment study area boundary, therefore, is defined by the 12-km radius.

     2.   Development of Subareas
         The study area is divided into  subareas to estimate risks to population subgroups
     within the study area, and to facilitate the  estimation of population risks.  Based on the
     results of the vapor dispersion modeling, 12 subareas are developed, as shown in Figure
     Vn-3.  The boundaries of the subareas are defined by concentric rings surrounding the
     facility at radii of 3 km, 7 km, and  12 km, and radials oriented northeast, southeast,
     southwest, and northwest.  The radials are oriented in this manner to include areas  with
     similar dispersion patterns within individual sectors.  As developed, the average vapor
     concentration in each subarea decreases  approximately two to three fold from the
     preceding subarea as the distance from the facility increases in any given direction.
     Thus, average risks in the outermost sector are approximately an order of magnitude
     less than the innermost sector in each direction.
Volume V
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     3.   Development of Subareas for Assessment of Fugitive Emissions
          Although population risks are not being evaluated in the assessment of fugitive
     organic vapor emissions from WTI, it is necessary to identify areas in the vicinity of
     the facility where impacts are predicted to be most significant.  Because the fugitive
     emission sources at the  WTI facility (with the exception of the CAB system stack) are
     ground-level (or near ground-level) sources, the maximum predicted impacts from these
     sources are generally on-site, with concentrations decreasing rapidly with distance from
     the source.  Thus, the area of interest for assessing the risks associated with fugitive
     emissions is the immediate vicinity of the site.
          The off-site impact of fugitive emissions is assessed within a 2,000-foot radius of
     the site.  This area is selected to include residential and commercial areas in East
     Liverpool near the facility, and the East Elementary school.  Based on a review of the
     air dispersion modeling, predicted air concentrations decrease significantly at distances
     greater than 2,000 feet from the facility. To account for concentration  variation with
     direction from the  site, the 2,000-foot radius for the fugitive emissions study area is
     sub-divided into four quadrants (north, south, east, and west), as indicated in
     Figure VII-4.

E.   Estimation  of Exposure Doses in Subareas

     1.   Estimation of Contaminant Dispersion/Deposition in Subareas
          In order to estimate the range of risks within a subarea, two estimates of dose are
     developed in this assessment: 1) area average dose, which represents the average
     exposure within a subarea; and 2) area maximum dose,  which is the estimated exposure
     at the location of maximum modeled concentration within a subarea.
          To estimate area average exposure, the average concentration and deposition rate
     of contaminants within the subarea is estimated. The air dispersion/deposition modeling
     predicts air concentrations  and particle deposition rates (wet and dry) at discrete
     locations (referred to as  receptor locations) on concentric circles around the facility to a
     distance of 50 kilometers from the facility.  Thus, each  of the 12 subareas (4 subareas
     for the fugitive emissions assessment) includes a number of these discrete receptor
     locations.  In the subareas  closest to the  facility (El, SI, Wl, and Nl in Figure VII-3),
     where there  is greater variation in predicted impacts, the receptor locations are  more
     closely spaced than farther from the facility, as described in Volume IV. As a  result, a
     greater number of receptors are contained within the subareas closer to the facility.  The
     average dispersion/deposition for a subarea is estimated  based on an area-weighted
     average of the dispersion or deposition predictions at receptors within the subarea.

Volume V                               VTT.IQ
-------
          The calculated average dispersion and wet and dry deposition factors (surface and
     mass-weighted) for each subarea are summarized in Tables vn-14 to VH-17.  In
     addition, dispersion and deposition factors at the point of maximum impact in  each
     subarea (defined as the location of maximum predicted vapor concentration) are
     compiled from the air dispersion/deposition modeling results and are summarized in
     Tables VH-14 to VH-17.

     2.   Estimation of Exposure Dose
          The predicted dispersion and deposition factors summarized in Table YE-14 to
     Vn-17 are used in the fate and transport models described in Chapter VI to predict
     contaminant media concentrations in each of the subareas.  Estimated media
     concentrations in each of the subareas  are summarized in Appendix V-ll.  Area average
     exposure doses are calculated using the dose equations (LADD and ADD), described
     earlier in this chapter.  The dose equations combine media concentrations (based on
     average concentrations in a subarea) summarized in Appendix V-ll and typical
     exposure factors in Appendix V-8. Area average doses for each subgroup of the
     population and for each exposure pathway are shown in Appendix V-12.  Maximum
     doses (LADDs and ADDs) for the exposed population subgroups are estimated at the
     location of maximum concentration within each subarea, as shown in Appendix V-13.
     An example of estimated chemical-specific area average doses (LADDs and ADDs) is
     provided in Tables Vn-18 and VII-19,  for a subsistence farmer in subarea El.

F.   Uncertainties
     In conducting the exposure assessment, several assumptions about general characteristics
of the population and individual behavior patterns are made. General characteristics of the
population include the identification of different subgroups that constitute the population in
the vicinity of the site.  A detailed review is conducted to ensure that the general population
is represented; in addition, subgroups that could be subject to high exposure because of their
particular behavior patterns are identified. Although all populations may not be represented
in  the analysis, the range of exposures that is evaluated is selected to constitute such a wide
range that exposures to a particular subgroup are likely to be represented within the  exposure
range evaluated.   Similarly, the exposure pathways  are selected to be as inclusive as feasible,
so that it is unlikely that any pathway of significance is excluded.
     In estimating the exposure dose for the exposed population, several exposure factors
such as inhalation rate,  soil ingestion rate and body weight are used. Typical values for
these parameters are used in the analysis. To account for the variability in these factors, the
90th percentile values for each of the exposure factors are determined, as summarized in

Volume V                              ^m *r\
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 Appendix V-8.  These high-end values are used in characterizing exposure to populations at
 the high-end of the risk distribution in assessing exposure variability in Chapter Vm.  In
 addition, in Chapter EX a quantitative evaluation of uncertainty and variability is conducted.
 which relies on the range of values developed for the exposure factors in assessing the
 overall impact  of uncertainty and variability on the estimated risks at the site.
     Specific assumptions used in the estimation of exposure dose are identified in
 Table  VII-20.  This table summarizes the key assumptions, a basis for each assumption, and
 the effect of each assumption of the results of the  HHRA.  The effect of each assumption on
 the estimated risks is characterized by estimating the direction (under- or overestimate) and
 relative magnitude (low, medium, high) of the effect.  As shown in Table VII-20. the
 selection of exposure factor values (especially for  the subsistence farmer) likely has the
 greatest effect of the assumptions used in this chapter.
Volume V                               VTT-91
-------
TABLE VIM
Typical Exposure Factors for which Site-Specific Data are Available1

Parameter
Percentage of residents with home gardens
Fraction from contaminated source
beef
pork
eggs
milk
vegetables
fruit
Deer meat ingeslion rate (g/day)
Adult
Resident
30

0.15
0.18
0.16
0.36
0.25
0.125
-
Child
Resident
30

0.15
0.18
0.16
0.36
0.25
0.125
-
School-Age
Child
30

0.15
0.18
0.16
0.36
0.25
0.125
-
Adult
Farmer
-

.
-
-
.
0.25
0.125
-
Child of
Farmer
-

_
-
.
_
0.25
0.125
-

Hunter
-

_
-
.
_
_
-
15
Notes
a = Method of estimation outlined in Appendix V 8
- = Site-specific data do not apply lo this population
Volume V
                                                        VH-22
-------
TABLE VD-2
Results of East Liverpool Board of Health
Vegetable Garden Surrey
Number of Home Gardens
VEGETABLES"
Beans, green
Beans, lima
Beets
Broccoli
Cabbage
Carrots
Cora
Cucumber
Lettuce
Onions
Onions, green
Peas
Peppers
Peppers, hot
Potatoes
Radishes
Spinach
Squash
Tomatoes
FRUITS'
Apples
Cherries
Grapes
Peaches
Strawberries
Watermelon
Downtown
1
0
0
0
0
0
0
0
0
1
0
0
2
0
0
0
2
1
4
Downtown
0
0
0
0
0
0
Dixonville
5
0
1
1
0
1
1
0
0
2
1
0
5
0
1
1
1
2
6
Dixonville
2
1
0
1
1
0
East
End
12
1
3
3
7
2
7
7
7
11
6
3
14
3
4
2
0
7
29
East
End
3
1
3
4
2
0
Northside
8
2
2
3
1
3
5
7
4
5
2
3
9
4
2
3
1
6
17
Northside
3
1
1
3
1
3
Pleasant
Heights
13
2
1
2
7
3
8
11
3
13
0
3
15
5
5
7
1
9
29
Pleasant
Heights
5
1
1
4
3
2
Lacroft
9
0
1
1
3
3
6
8
4
6
2
1
8
1
t
3
0
2
15
Lacroft
2
1
0
0
0
1
TOTALS
48
5
8
11
18
12
27
33
18
38
11
10
53
13
14
16
5
27
100
TOTALS
15
5
5
12
7
6
Notes- f
a - Only those vegetables and fruits identified by at least 5 percent of respondents are included.
Source: East Liverpool Board of Health (personal commurucation).
Volume V
-------
TABLE Vn-3
Portion of Diet from Home Garden*
Percentage of
Vegetable Diet
<25%
25% -50%
50% - 75%
>15%
Percentage of
Fruit Diet
<25%
25% -50%
50% - 75%
>75%
Number of Homes
Downtown
3
1


Downtown
1



Dixonville
4
2


Dixonville
2



East
End
13
11
4
1
East
End
5
1

1
Northside
6
11

1
Northside
3
2


Pleasant
Heights
17
9
3

Pleasant
Heights
11



Lacroft
6
8

1
Lacroft
5



TOTAL
40
42
7
3
TOTAL
27
3
0
1
a - Based on the results of the East Liverpool Board of Health Home Garden Survey.
Source: East Liverpool Board of Health (per»onal communication)
Volume V
-------
TABLE VD-4
Summary of Ohio River Recreational Fishing Study Data
Parameter
Estimated Number of Fish Caught*
Estimated Number of Fish Kept"
Estimated Number of Angler Hours"
WTI Facility
Viciniryb
400.000
63,000
180.000
Farther
Downstream of
\VT1
2.800.000
300.000
1.600.000
Fish Type and Size Data for Survey Locations in WTI Vicinity
Types of Fish
Bass
Percids
Catfish
Carp
Other
% of Fish
Kept
88%
8%
1%
<0.1%
3%
Avg. Sized
(inches')
7 - 13
11 - 13
12 - 17
17 - 18
6 - 16
Notes:
a - Values extrapolated by ODNR from raw data.
b - Represents data collected in ODNR (1994a) ttudy from iurvey areas #1 to #4 (Ohio River Mile (ORM) 40. 1 to
69.5). The WTI facility is at ORM 4 1.5.
c - Represents data collected in ODNR (1994a) study from iurvey areas #5 to #32 (ORM 69.5 to 341)
d - Approximated from fish length daU compiled by ODNR (1994a)
Volume V
                                            \rn-ic;
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TABLE VH-5
State-wide Beef Statistics
Parameter
Total Cattle/Calves (C,.)
Beef Cows
Milk Cows
Beef Heifers (replacement)
Milk Heifers (replacement)
Other Heifers
Steers
Bulls
Calves
Plant Cattle Slaughter (PS,,,,)
Calves Born (B)
Calf Marketed (M^)
Plant Calf Slaughter (PS^)
Number of Head (thousands)
Ohio*
1,610
355
315
72
159
83
229
30
367
185
560
150
62
Pennsylvania*
1,850
201
659
44
293
46
210
31
366
969
229b (estimate)
780
291
168
West Virginia"
520
262
23
50
9
16
54
17
89
16
250
128
NA
Notes.
NA - Not available
a - State-wide agricultural statistics obtained from the Agricultural Statistics Service for Ohio, Pennsylvania, and West Virginia
(ODA 1994; PDA 1994; WVDA 1994) Total cattle/calves data are for January 1, 1993; all other data are for most recent
calendaryear available (1993 for Ohio, 1992 for Pennsylvania and West Virginia).
b - This value is an estimate of the number of Pennsylvania-bred cattle that are slaughtered in the state. 740 thousand head
slaughtered annually in two large eastern Pennsylvania slaughter houses are not included in this number
Volume V
-------
TABLE VII-6
Estimated County Beef Statistics
Parameter
Total Cattle/Calves (Crf
Plant Cattle Slaughter
(PS-d)b
Calves Bom (B)°
Plant Calf Slaughter (PS^Y
Number of Head in County
Columbiana,
Ohio
26,000
3,000
9,000
1,000
Beaver,
Pennsylvania
11,500
1,400
4.800
1.000
Hancock.
West Virginia
1.200
37
580
87
Note:
a - ODA 1994; as of January 1, 1993.
b - Based on state-wide data: PS^C,. (185/1,610 = 0.12)
c - Based on state-wide data: B/C,. (560/1 ,610 = 0.35)
d - Based on sute-wide data: PS,^/B (62/560 = 0.1 1)
Volume V
                                               VTT.1-7
-------
TABLE VH-7
Summary of Beef Farming Data
Beaver Valley Nuclear Power Station Survey
Farm Location with Respect to Power Plant
(miles)
1.70 N
3.86N
3.94 N
3.94 N
3.03 NNE
4.70 NNE
4.93 NNE
3.11 NE
3.94 NE
2.62 E
3.39 E
3.98E
2.94 ESE
2.96 ESE
3.52 ESE
1.78 SE
2.35 SE
2.75 SE
3.07 SE
3.07 SE
3.50 SE
3.56 SE
1.10SSE
3.14SSE
4.53 SSE
4.57 SSE
5.00 SSE
2.16 S
Number of Beef Cattle
9
4
40
18
10
14
11
15
6
6
3
17
10
2
2 '
•}
^
11
2
4
25
16
15
19
3
9
6
12
2
Volume V
-------
TABLE Vn-7 (continued)
Summary of Beef Farming Data
Beaver Valley Nuclear Power Station Surrey
Farm Location with Respect to Power Plant
(miles)
2.24 S
2.35 S
2.38 S
2.82 S
3.83 S
4.70 S
5.04 S
1.82SSW
2.20 SSW
2.69 SSW
3.60 SSW
4.55 SSW
4.60 SSW
4.74 SSW
1.55 SW
2.73 SW
2.77 SW
2.80 SW
3.11 SW
3.14SW
4.09 SW
4.83 SW
1.63 WSW
2.54 WSW
2.54 WSW
2.84 WSW
2.88 WSW
3.26 WSW
Number of Beef Cattle
2
3
1
1
10
7
32
1
5
6
12
4
12
20
105
10
28
6
8
6
21
30
95
7
15
'6
30
8
Volume V
                                            VTT-OQ
-------
TABLE VU-7 (continued)
Summary of Beef Fanning Data
Beaver Valley Nuclear Power Station Survey
Farm Location with Respect to Power Plant
(miles)
3.41 WSW
3.83 WSW
4.51 WSW
2.52 W
3.18 W
3.52 W
2.84 WNW
3.11 WNW
3.68 WNW
2.46 NNW
4.44 NNW
TOTAL (67)
Source- Porter Consultants Inc. (PCI) 1992.
Number of Beef Cattle
15
3
23
6
1
23
2
13
3
10
26
909

Volume V
-------
                                                  TABLE Vn-8
                                              State-wide Milk Data*
                                                    Ohio
                    Pennsylvania
                   West Virginia
     Milk Cows (x 103 head)
  315
 655
     Annual Milk Production (x 106 Ibs)
 4,625
10,364
 278
     Annual Marketing (x 10* Ibs)
 4.625
10,364
 278
              Fed to Calves on Farm
   20
  70
              Consumed on Farm
   15
  30
              Sold to Plants/Dealers
 NAb
(4,470)
9,999
NAb
(265)
              Sold to Consumers
 NA"
 (120)
 265
NAb
 (7)
     Notes-
             State-wide agricultural statistics obtained from the Agricultural Statistics Service for Ohio, Pennsylvania, and West
             Virginia (ODA 1994; PDA 1994; WVDA  1994).
             Available Ohio and West Virginia sales data were not divided between sales to plants/dealers and direct sales to
             consumers The numbers in parenthesis represent estimated values based on the distribution of sales between sales to
             Plants/dealers and direct sales to consumers exhibited in Pennsylvania data.
Volume  V
-------
TABLE VD-9
Estimated County Dairy Statistics*

Milk Cowsk
Annual Milk Production (x 103 Ibs)
Columbiana,
Ohio
11,800
179,800C
Beaver,
Pennsylvania
3.000
41.700''
Hancock,
West Virginia
<50
604C
Annual Marketing' (x 103 Ibs)
Fed to Calves on Farm
Consumed on Farm
Sold to Plants/Dealers
Sold to Consumers
770
580
173,800
4,700
280
120
40,200
1,100
9
4
576
15
Notes-
a - County data estimated based on state data and the fraction of the total state herd in county.
b - ODA 1994; PDA 1994; WVDA 1994
c - Available Ohio agricultural statistics provide county-specific data on milk told. Milk production was estimated
based on state-wide data.
d - PDA 1994
e - Estimated based on fraction of state milk cow herd in county multiplied by the total milk produced in the sute
f - Marketing values do not necessarily sum to total production due to rounding .
Volume V
-------
TABLE VII-10
Summary of Dairy Farming Data
Beaver Valley Nuclear Power Station Survey
Farm Location with Respect to Power Plant
(miles)
0.98 ESE
2.24 S
4.83 S
2.16 SSW
3.56 SSW
4.55 SSW
5.11 SSW
5. 15 SSW
3.75 WSW
3.83 WSW
3.86 WSW
TOTAL (11)
Number of Cows
2
1
1
60
2
1
55
80
35
50
45
332
Number Milked
1
0
0
43
0
1
40
55
33
34
35
242
Daily Milk
Production
(gallons)
1.5
0
0
150
0
8
115
185
210
150
150
969.5
Dairy Milk
Production
(gallons) per Cow
1.5
-
-
3.5
.
8
2.9
3.4
6.4
4.4
4.3
4.0
Source: Porter Consultants, Inc. (PCI) 1992
Volume V
                                                                 Vll-33
-------
TABLE VD-11
Number of Dairy Farmers and Monthly Milk Production
for Three Counties Surrounding WTI Facility (May 1994)'

1 - 30,000 (Ibs)
Dairy fanners
Production (Ibs)
30.001 - 60,000 (Ibs)
Dairy farmers
Production (Ibs)
60,001 - 90,000 (Ibs)
Dairy fanners
Production (Ibs)
90,001 - 120,000 (Ibs)
Dairy farmers
Production (Ibs)
120,001 - 150,000 (Ibs)
Dairy farmers
Production (Ibs)
150,001 & over (Ibs)
Dairy farmers
Production (Ibs)
Total County
Dairy farmers
Production (Ibs)
Columbians County,
Ohio
22
492,698
48
2,188,406
38
2,793,815
20
2,008,339
14
1,929,043
22
4,769.800
164
14,182,101
Beaver Counry,
Pennsylvania
10
215.490
21
914,075
14
977,058
9
931,132
4
518,946
1
R
59
3,556,701"
Hancock Count) ,
West Virginia
No dairy farmers
listed
Notes
a - From records of Federal Milk Marketing Orders, obtained from personal communication with J. Rourke (personal
communication 1994). It should be noted that, although from different sources, milk production data in this table and in
Table VIJ-9 are not inconsistent.
b - Toul county production for Beaver County. PA. does not include production volume of producer with milk production of
greater than 150,000 pounds.
R - Restricted data
Volume V
-------
TABLE VD-12
Estimation of Meat from Deer Hunted Locally
County
Columbiana
Beaver
Hancock
TOTAL
Annual Deer Harvest*
2,149
4,452
787
7,388
Deer Meat Available"
dbs)
85,960
178.080
31,480
295.520
Numbers of Hunters"
4.315
17.013
3.365
24.693
Notes.
a - ODNR 1994b, PDNR 1994, WDNR 1994a
b - WVDNR 1994b
Volume V
-------
TABLE VE-13
Summary of County Population Data
County
Columbiana, Ohio
Beaver, Pennsylvania
Hancock, West Virginia
Total Population*
108,276
186,093
35,233
Number of Farms"
977
512
75
Estimated Farming
Population'
2.570
1.300
191
Sources
a - CACI 1992
b - Ohio: USDC 1993a; Pennsylvania: USDC 1993b; West Virginia USDC 1993c
c - Estimated based on the average number of individuals per household (2.63 per household in Columbiana; 2.54 per
household in Beaver; and 2.54 per household in Hancock; CACI 1992) and the number of farms in coum> .
Volume V
-------
TABLE VD-14
Average and Maximum Air Dispersion/Deposition Impacts in
East Subareas
Subarea
Concentration
Estimator
El
Average
Maximum
E2
Average
Maximum
E3
Average
Maximum
Vapor
Dispersion
Gig/m'-g/s)
0.29
0.91
0.14
0.31
0.060
0.092
Surface Avg Deposition*
(g/m*-yr per g/s)
Wet
0.014
0.025
0.0039
0.0065
0.0017
0.0021
Dry
0.0021
0.0052
0.00098
0.0018
0.00039
0.00051
Mass Avg Deposition*
(g/nr-y per g/s)
Wet
0.011
0.018
0.0032
0.0052
0.0015
0.0018
Dn,
0.00097
0.0025
0.00046
0.00084
0.00019
0.00025
Note.
a - Organic compounds adsorb onto the outer surface of airborne particles as condensation occurs in the cooler regions of
the post-combustion zone (i.e., surface distribution). Metals are assumed to be homogeneously dispersed throughout
the entire particle (i.e., mass distribution) because they may form particles themselves rather than condensing onto
existing particles. Therefore, for orgamcs, deposition on particles is a function of the total surface area of panicles
emitted from the suck; whereas, for metals, deposition is a function of the total mass. The amount of a substance
deposited on the ground surface is dependent upon the type of distribution (surface or mass) assumed
Volume V
-------
TABLE VIMS
Average and Maximum Air Dispersion/Deposition Impacts in
North Subareas
Subarea
Concentration
Estimator
Ml
Average
Maximum
N2
Average
Maximum
N3
Average
Maximum
Vapor
Dispersion
Gig/mJ-g/s)
0.14
0.38
0.055
0.14
0.024
0.038
Surface Avg Deposition*
(g/m2-yr per g/s)
Wet
0.0075
0.025
0.0023
0.0049
0.0011
0.0016
Dry
0.00074
0.0012
0.00027
0.0010
0.00011
0.00027
Mass Avg Deposition"
(g/m:-y per g/s)
Wet
0.0057
0.019
0.0018
0.0039
0.00096
0.0014
Dr>
0.00037
0.00070
0.00013
0.00047
0.000055
0.00013
Note:
a - Organic compounds adsorb onto the outer surface of airborne particles as condensation occurs in the cooler regions of
the post-combustion zone (i.e., surface distribution). Metals are assumed to be homogeneously dispersed throughout
the entire particle (i.e., mass distribution) because they may form particles themselves rather than condensing onto
existing particles. Therefore, for organics, deposition on panicles is a function of the total surface area of panicles
emitted from the suck; whereas, for metals, deposition is a function of the total mass. The amount of a substance
deposited on the ground surface is dependent upon the type of distribution (surface or mass) assumed
Volume V
-------
TABLE VH-16
Average and Maximum Air Dispersion/Deposition Impacts in
South Subareas
Subarea
Concentration
Estimator
SI
Average
Maximum
S2
Average
Maximum
S3
Average
Maximum
Vapor
Dispersion
Gig/m'-g/s)
0.14
0.51
0.066
0.14
0.029
0.042
Surface Avg Deposition*
(g/m2-yr per g/s)
Wet
0.0051
0.025
0.0012
0.0030
0.00057
0.00095
Dry
0.00074
0.0024
0.00030
0.00066
0.00013
0.00019
Mass Avg Deposition"
(g/nr-y per g/s)
Wet
0.0042
0.021
0.00098
0.0026
0.00048
0.00082
Dn
0.00036
o.ooi:
0.00015
0.00033
0.000066
0.00010
Note
a - Organic compounds adsorb onto the outer surface of airborne particles as condensation occurs in the cooler regions of
the post-combustion zone (i.e., surface distribution). Metals are assumed to be homogeneously dispersed throughout
the entire particle (i.e., mass distribution) because they may form particles themselves rather than condensing onto
existing particles. Therefore, for organics, deposition on particles is a function of the total surface area of particles
emitted from the stack; whereas, for meuls, deposition i» a function of the total mats. The amount of a substance
deposited on the ground surface is dependent upon the t> pe of distribution (surface or mass) assumed .
Volume V
-------
TABLE Vn-17
Average and Maximum Air Dispersion/Deposition Impacts in
West Subareas
Subarea
Concentration
Estimator
Wl
Average
Maximum
W2
Average
Maximum
W3
Average
Maximum
Vapor
Dispersion
Otg/m3-g/s)
0.20
0.59
0.096
0.21
0.044
0.068
Surface Avg Deposition*
(g/mj-yr per g/s)
Wet
0.0077
0.014
0.0023
0.0041
0.0011
0.00089
Dry
0.00084
0.0022
0.00038
0.00082
0.00017
0.00026
Mass Avg Deposition'
(g/nr-y per g/s)
Wet
0.0058
0.0050
0.0018
0.0032
0.00094
0.00073
Dn
0.00044
0.0012
0.00020
0.00044
0.00009
0.00014
Note:
a - Organic compounds adsorb onto the outer surface of airborne particles as condensation occurs in the cooler regions of
the post-combustion zone (i.e., surface distribution). Metals are assumed to be homogeneously dispersed throughout
the entire particle (i.e., mass distribution) because they may form particles themselves rather than condensing onio
existing panicles. Therefore, for organics, deposition on particles is a function of the total surface area of particles
emitted from the suck; whereas, for metals, deposition is a function of the total mass. The amount of a substance
deposited on the ground surface is dependent upon the type of distribution (surface or mass) assumed
Volume V
-------
TABLE VII-18
Chemical-specific Lifetime Average Daily Dose (LADD) for Carcinogens
Adult Subsistence Fanner in Subarea El (Area Average Concentration)
Chemical
2,3,7,8-TCDD
1,2,3,7, 8-PeCDD
1,2,3,4,7,8-HxCDD
1 ,2,3,6, 7,8-HxCDD
1,2,3,7,8,9-HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1, 2,3,7, 8-PeCDF
2,3,4,7,8-PeCDF
1, 2,3,4,7, 8-HxCDF
1,2,3,6,7,8-HxCDF
1,2,3,7,8,9-HxCDF
2,3,4,6,7,8-HxCDF
1,2,3,4,6, 7, 8-HpCDF

1, 2,3,4,7, 8,9-HpCDF
OCDF
Soil Ingestion
and Dermal
Contact mg/kg-d
1 x 10"
5 x 10 •'•
5 x 10 -'«
1 x 10"
6 x 10"
7 x 10"
3 x 10"
9 x 10"
3 x 10"
4 x 10"
9 x 10"
8 x 10"
2 x 10 "
9 x 10"
5 x 10"
7 x 10"
1 x 10"
Total Meat and
Egg Ingestion"
mg/kg-d
5 x 10"
7 x 10"
5 x 10"
1 x 10"
2 x 10"
1 x 1012
3 x 10'°
1 x 10"
7 x 10"
4 x 10 l2
2 x 10"
4 x 10 l2
9 x 10"
3 x 10 l2
2 x I012
4 x 10"
2x 10"
Total Dairy
Product
Ingestionb
mg/kg-d
3 x 10 "
6 x 10"
4 x 10"
1 x 10"
1 x 10"
1 x 10'2
2 x 10'°
1 x 10"
5 x 10"
3 x 1012
2 x 1012
3 x 10"
6 x 10"
2 x 1012
1 x 1012
3 x 10"
2 x 10"
Total Fruit and
Vegetable
Ingestion0
mg/kg-d
1 x 10"
2 x 10-"
3 x 10"
8 x 10"
9 x 10"
5 x 10"
6 x 10"
2 x 10"
1 x 10"
1 x 10"
1 x 10"
2 x 10"
5 x 10"
2 x 10"
5 x 10"
4 x IOM
1 x 10"
River Water
Ingestion and
Dermal Contact
mg/kg-d
1 x 10"
5 x 10 -"
7 x 10"
1 x 10"
2 x 10 -"
6 x 10"
3 x 10"
1 x 10"
4 x 10"
6 x 10"
1 x 10"
1 x 10"
3 x 10"
1 x 10"
6 x 10"
8 x 10"
6 x 10"
Infant Breast
Milk
Ingestion
mg/kg-d
5 x 10"
•*.
8 x 10"
5 x 10"
1 x 10"
2 x 10"
2 x 10"
3 x 10'°
2 x 10"
7 x 10"
4 x 10"
2 x 10"
4 x IO'2
9 x 10"
3 x 10 l2
2 x 10"
5 x 10"
3 x 10"
Volume V
                                                             VII-41
                                                               /  \
-------
TABLE VH-18 (continued)
Chemical-specific Lifetime Average Daily Dose (LADD) for Carcinogens
Adult Subsistence Farmer in Subarea El (Area Average Concentration)
Chemical
Telrachlorobiphenyl
Hexachlorobiphenyl
Heptachlorobiphenyl
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethylhexyl)phthalate
Carbon telrachloride
Dibenz(a,h)anthracene
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Indeno( 1 ,2,3-cd)pyrene
Arsenic
Beryllium
Soil Ingestion
and Dermal
Contact mg/kg-d
1 x 10 "
2 x 10"
2 x 10"
3 x 10"
1 x 10"
1 x 1012
8 x 10"
8x 1012
7 x 10 "
1 x 10"
3 x 10"
9 x 10"
3 x 10"
8 x 10 u
Total Meat and
Egg Ingestion"
mg/kg-d
I x 10"
8 x 10"
2 x 10 10
1 x 10-*
8 x 10»
1 x 10^
1 x 10"
2 x 10'
9 x 10 "
1 x 10'°
2 x 10"
2 x 10'
2 x 10 10
1 x 10"
Total Dairy
Product
Ingestion"
mg/kg-d
7 x 10"
5 x 10"
1 x 10'°
2 x 10*
9 x 10'
1 x 10*
7 x 10"
2 x 10'
1 x 10"
7 x 10-"
1 x 10"
2 x 10'
2 x 10"
2 x 10"
Total Fruit and
Vegetable
Ingestion0
mg/kg-d
3 x 10"
3 x 10"
9 x 10 "
\ x 10'
5 x 10'°
5 x 107
2 x 10'
9 x 10'2
5 x 1013
J x 10'°
7 x 10"
1 x 10"
8 x 10"
4x10"
River Water
Ingestion and
Dermal Contact
mg/kg-d
2 x 10"
4 x 10"
9 x 10"
3 x 1014
1 x 10"
2 x 10"
5 x 10"
2 x 10"
3 x I017
2 x 1011
4 x 1014
2 x 1011
I x 10"
2 x 10'"
Infant Breast
Milk
Ingestion
mg/kg-d
1 x 10" \
7 x 10"
2 x 10 In
9x 10*
6 x 10"
1 x 10*
2x I012
5 x 10*
8 x 10"
5 x 10 10
2 x 10"
4 x 10s
NA
NA
Notes:
a - Based on ingestion of beef, pork, chicken, other poultry, and eggs
b - Based on ingestion of milk, cheese, milk desserts, yogurt, cream, and butter
c - Based on ingestion of exposed, protected leafy, and root produce, and exposed and prolecle'l fruil
Volume V
                                                             VII-42
-------
TABLE VII-19
Chemical-specific Average Daily Dose (ADD) for Noncarcinogens, Adult Subsistence Farmer in Subarea El
(Area Average Concentration)
Chemical
Bis(2-ethylhexyl)phthalate
Carbon tetrachloride
Di(n)octyl phthalate
Heptachlor
Heptachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Mercury
Nickel
Selenium
Soil Ingestion
and Dermal Contact
mg/kg-d
4 x 10 l2
3 x ia"
1 x 1012
2 x 10 "
4 x ia"
i x ia'°
2 x ia12
7 x ia"
3 x ia12
1 x 10'°
1 x 10 10
3 x 10"
2 x 10 12
8 x 10'2
i x ia9
1 x 10"
2 x 109
Total Meat and Egg
Ingestion"
mg/kg-d
4 x 10^
3 x 10 12
4 x 10^
3 x 10"
4 x 10 10
9 x 10"
5 x 10 l2
3 x 107
3 x 10"
6 x 10 10
5 x 10'°
4 x 10"
2 x 10 "
5 x 10"
4 x 109
6 x 10'°
1 x 107
Total Dairy Product
Ingestionb
mg/kg-d
4x 10-6
2 x 10 '2
5 x 10^
3 x ia"
3 x 10'°
5 x 10"
3 x 10"
3 x 107
1 x 10"
5 x 10"
1 x 10'
9 x 10"
3 x 1012
3 x 10"
6 x 10'
1 x 10'°
5 x 10s
Total Fruit and
Vegetable Ingestion0
mg/kg-d
2 x 10^
6 x 109
4 x 107
2 x 10 l2
4 x 10'°
3 x 10'°
6 x 10'2
6 x 10'°
7 x 10"
3 x 10'°
2 x 109
1 x 10"
2 x 10'°
5 x I012
2 x I07
2 x K)1"
1 x 10*
River Water
Ingestion and
Dermal Contact
mg/kg-d
6 x 10"
2 x 10"
1 x 10"
1 x 10"
7 x 10"
2 x 10n
5 x 10"
4 x 10 12
2 x I016
5 x 10"
9 x 10"
5 x 10'"
2 x 10"
1 x 10 '"
1 x 10 n
5 x 10"
7 x 10"
Volume V
                                                              VII-43
-------
TABLE VI 1-1 9 (continued)
Chemical-specific Average Daily Dose (ADD) for Noncarcinogens, Adult Subsistence Fanner in Subarea El
(Area Average Concentration)
Chemical
Silver
Thallium
Zinc
Soil Ingestion
and Dermal Contact
mg/kg-d
I x 10"
5 x 10'°
7 x 10-"
Total Meat and Egg
Ingestion"
mg/kg-d
4 x ia10
5 x 1O"
3 x 10'°
Total Dairy Product
Ingestionb
mg/kg-d
9 x 109
2 x 109
2 x 10'°
Total Fruit and
Vegetable Ingestion'
mg/kg-d
6 x 10'°
1 x 10'°
4 x 10*
River Water
Ingestion and
Dermal Contact
mg/kg-d
7 x 10"
6 x 1015
5 x 10'5
Notes:
« - Based on ingestion of beef, pork, chicken, other poultry, and eggs
b - Based on ingestion of milk, cheese, milk desserts, yogurt, cream, and butter
c - Based on ingestion of exposed, protected leafy, and root produce, and exposed and protected fruit
Volume V
VJI-44
-------
TABLE VII-20
Key Assumptions for Chapter VII
(Estimation of Exposure Dose)
Assumption
Exposure to organic vapor fugitive emissions is
evaluated only via the inhalation pathway
The East Liverpool Board of Health estimates that
30% of local residents have home gardens. Their
survey of 100 residents with gardens is
representative of local gardening practices and
provides reasonable data to estimate the fraction of
diet that is homegrown
Fishing practices near the WTI facility are
represented by four fishing study areas. Annual
data are based on April to November data. The
average weight of fish is estimated by the
ORSANCO electroflshing survey of average weight
of fish.
The number of Pennsylvania-bred cattle is estimated
State-wide cattle statistics are representative of local
farming practices (i.e., beef raising and slaughter
practices are uniform across all parts of the state)
State-wide milk production estimates apply to local
production and the distribution of milk sold to
plants/dealers and directly to consumers is the same
in Ohio and West Virginia as Pennsylvania
Basis
Fugitive emissions are volatile chemicals, which
are not likely to bioconcentrate.
Professional judgment on best available data.
Professional judgment on best available data.
Professional judgment. The estimate is consistent
with data from Ohio and West Virginia.
Discussion with local agricultural agents indicated
that most calves are sent out of the area for
slaughter.
Discussion with local agricultural agents indicated
that local dairy farming practices do not differ
from state practices.
Magnitude of
Effect
low
low
low
low
low
low
Direction of Effect
underestimate
'*L
unknown
unknown
unknown
overestimate
unknown
Volume V
    /   \
VII 45
  f
-------
TABLE VH-20 (continued)
Key Assumptions for Chapter VII
(Estimation of Exposure Dose)
Assumption
Exposure factors represent the behavior of the
various populations
Basis
Site-specific values are used whenever possible,
otherwise, EPA-defauH values are used - the 50th
percentile for average exposures and the 90th
percentile for high-end exposure. Factors for the
subsistence farmer likely overestimate risks
because this assessment conservatively assumes
the food products this population consumes are
100% locally-raised, which is unlikely.
Magnitude of
Effect
medium
Direction of Effect
overestimate
'».
Notes:
low = less than a factor of two
medium = a factor of two to ten
high = greater than a factor of ten
Volume V
VII-46
-------
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               4394S 43930 ^  4396S


                L  .1 T *
Number of dairy (arms
within ZIP code
        NUMBER OF DAIRY FARMS BY ZIP CODE
            IN VICINITY OF THE WTI FACILITY
-------
                              V/i-w
OHIO
                                              PE\\SYL\'A\IA
                                              ^C3"?
       SUB-AREAS WITHIN  RISK ASSESSMENT STUDY AREA
Figure
 VII-3
-------
                                      a-so
                                             Approximate
                                               Facility
                                              Boundary
 IXPLANATION
   Fugitive
     1  Open wastewater tank
     2  Truck wash
     3  Organic waste  tanK farm
     4  Carbon  aasorotion oea
     5  Ash  handling
 -900—  Isopleth of eauai vertica1 elevation,  in feet
LOCATION  OF FUGITIVE EMISSION  SOURCES  AND QUADRANTS
  USED  TO  EVALUATE  AVERAGE  FUGITIVE EMISSION  RISKS
-------
                      Vffl.  RISK CHARACTERIZATION
 A.    Introduction
       In the risk characterization step of the risk assessment process, the chemical toxicity
 values (summarized in Chapter HI) are combined with dose estimates for each of the various
 exposure pathways and population subgroups (described in Chapter YE) to evaluate both
 carcinogenic risks and the potential for noncarcinogenic health effects.  Beyond the
 quantitative aspects of the risk assessment, risk characterization is also intended to place the
 estimated risks in context through a discussion of the qualitative elements of the risk
 assessment, including a discussion of the major factors  influencing the risk estimates,
 underlying assumptions, and the rationale for these assumptions.  In addition, the risk
 characterization generally includes a discussion of the uncertainty and variability associated
 with the quantitative results.  Therefore, a table of the key assumptions,  as described in
 Volume n, is presented as part of the uncertainty section of this chapter. A quantitative
 analysis of uncertainties is presented in Chapter IX.
       Based on a review of the Project Plan for the WTI Risk Assessment (U.S. EPA
 1993b), the Peer Review  Panel made several recommendations regarding risk
 characterization.  These recommendations include the following:

 •     Assessment of Risks Associated with Fugitive Emissions - The Project Plan (U.S.
       EPA 1993b) proposed that fugitive emissions be evaluated on a qualitative  level.
       Based on recommendations of the Peer Review Panel, a quantitative analysis of
       carcinogenic risks and the potential for noncancer health effects is conducted for  four
       sources of possible fugitive emissions from the WTI facility.  This chapter
       summarizes the results of the fugitive emissions analysis, which focuses on exposures
       within 2,000 feet of the WTI facility where potential impacts are most significant
       based  on the air dispersion modeling.

 •     Additivitv of Risk - The Peer Review Panel  commented that additivity of risks should
       be considered in the risk characterization, including an evaluation of synergistic and
       antagonistic effects of exposure to chemicals in combination.  In this chapter, additive
       risks are estimated for the combination of all chemicals evaluated in each exposure
       pathway, and for the combination of all pathways evaluated for each population
Volume V
                                        \rrn_i
-------
       subgroup.  A quantitative evaluation of synergistic and antagonistic effects is not
       performed due to limitations in available data and methodologies for characterizing or
       quantifying these effects at the exposure levels estimated in the vicinity of WTL

 •     Evaluation of Additional High-end Subgroups - The  Peer Review Panel identified a
       number of additional subgroups of the exposed population that may be at a higher risk
       due to behavior patterns, proximity to the facility, or lexicological sensitivity.  An
       evaluation of additional high-end  subgroups is presented  in Appendix V-5. Based on
       this analysis, an additional potential high-end subgroup, deer hunters, was identified.
       An evaluation of human health risks associated with consumption of deer meat
       obtained from the vicinity of the WTI facility is presented in this chapter.

 •     Uncertainty and Variability - The Peer Review Panel recommended that as part of the
       characterization of risks, the uncertainty and variability associated with estimated risks
       also be presented.  A quantitative uncertainty and variability analysis for the HHRA,
       is presented as a separate chapter (Chapter IX). Issues that affect the uncertainty of
       the risk characterization are discussed  qualitatively in Section F of this chapter.

       The following sections present the results of the risk assessment for exposure to stack
emissions and fugitive releases.  Risks associated with exposure to stack emissions and
fugitive emissions are characterized separately.

B.     Estimation of Risks Due to Stack Emissions
       Substances of potential concern emitted from the incinerator stack at the WTI facility
disperse in the atmosphere as well as deposit on soils in the vicinity of the facility.  Exposure
to these substances by individuals living and working in the  area surrounding the WTI
facility can occur through various pathways and may result in adverse health effects.  To
estimate the likelihood of such effects, cancer risks and the potential for noncarcinogenic
effects are characterized based on a combination of estimated exposure doses and U.S. EPA-
published  chemical-specific toxicity values, as described below.

       1.      Methodology for Estimating Individual Cancer Risk
              The excess lifetime cancer risk  resulting from the modeled exposure to a
       specific carcinogenic chemical is calculated by multiplying the lifetime average daily
       dose  (LADD), which is estimated as described in Chapter Vn, by the risk per unit
       dose, or slope factor (discussed in Chapter HI), as follows:
Volume V
-------
                     Risk;          =     (LADDiXSF;)                            (Vm-1)

        where:
              Risk,         =     lifetime probability of developing cancer due to exposure
                                  to chemical i in stack emissions from the WTI facility
              LADDj       =     lifetime average daily dose to chemical i, mg/kg-day
              SFj           =     carcinogenic slope factor for chemical i, (mg/kg-day) :

              In cases of multiple chemical exposures, it is assumed that cancer risks  are
        additive (U.S. EPA 1986b).  Accordingly, the cancer risk estimates for each exposure
        pathway are developed by summing the risk calculated for the individual chemicals.
        In addition, risk estimates are summed across exposure pathways to develop total
        cumulative risks for a population subgroup, in cases when it is reasonable to assume
        that individuals in a subgroup could typically be exposed through all such pathways.

        2.     Methodology for Estimating Individual Noncancer Effects
              Unlike the measure of risk used for carcinogens, the measure used to describe
        the potential for noncarcinogenic effects to occur is not expressed as a probability of
        experiencing an adverse effect (U.S. EPA 1986b). Instead,  the potential for adverse
        noncancer effects is expressed as the ratio of the calculated dose to the dose below
                                       s
        which adverse effects are not anticipated (or the Reference Dose).  If this ratio
       exceeds 1.0 (unity), it is assumed that the potential exists for noncancer  health effects.
       For oral exposures, the following equation is used:

                    HQ;   =      ADD/RfD,                                    (VHI-2)

       where:
                    =     hazard quotient for chemical i
             ADD  =     average daily dose to chemical i (all appropriate pathways
                           combined), mg/kg-day
             RfD   =     reference dose for chemical i,  mg/kg-day

             For inhalation exposures, reference air concentrations (RACs), which account
       for exposure to background sources of chemicals with noncarcinogenic effects, are
       developed to assess the potential for noncancer effects. In order to compare the
       RACs, expressed in units of milligrams per cubic meter (mg/m3), with the ADD, the
       RACs are converted to inhalation reference doses, in units of milligram per kilogram-
Volume V
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       day (mg/kg-day), based on a standard inhalation rate (20 mVday) and body weight (70
       kilograms) (U.S. EPA 1990b). The hazard quotients are calculated using the above
       equation and the inhalation RfDs.
             The assessment of overall potential for noncancer effects posed by
       simultaneous exposure to multiple chemicals is conducted using the Hazard Index
       approach developed in U.S. EPA's Guidelines for the Health Risk Assessment of
       Chemical Mixtures  (U.S. EPA 1986b) and described in U.S. EPA's Risk Assessment
       Guidance for Superfund (U.S. EPA 1989b). As a first screening, the HQ values for
       all individual chemicals associated with a given exposure pathway are summed to
       provide an indication of the potential for noncancer effects posed by multiple chemical
       exposure.  This sum of the HQ values for individual chemicals is referred  to as the
       Hazard Index (HI).  The HI approach assumes that multiple sub-threshold exposures
       could result in an adverse effect,  and that a reasonable criterion for evaluating the
       potential adverse effects is the sum of the HQ values (U.S. EPA 1986b). In cases
       where the overall HI exceed unity, chemicals are segregated by target organ effect
       and mechanism of toxicity to derive HI values for each type of effect, as
       recommended by U.S. EPA (19.86b). A summary of the target organs for the
       substances of potential concern with potential adverse noncancer effects is provided in
       Table Vm-1.

       3.     Methodology for Estimating Population Cancer Risk
             In addition to individual risk, the total cancer risk burden for the exposed
       population in the vicinity of the facility is determined for incinerator stack
       emissions.1  As described in Chapter Vn, a study area has been developed
       comprising of 12 subareas surrounding the WTI facility.  Cancer risks for each of the
       identified subgroups (e.g., farmers, adult residents, child residents, etc.) are estimated
       within each subarea  using the procedures described above.  The total population
       cancer risk associated with incinerator stack emissions is then calculated across all
       subareas and subgroups in the study area using the following equation:
    1 Given the relatively small area potentially affected by fugitive emissions based on the
atmospheric dispersion modeling, population risks are not characterized for fugitive
emissions sources.
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                                                 n  m
                       Population Cancer Risk = £ £ (PJd&kJ               (Vm-3)
                                                i-l ;-l

       where:
              P(J            =     population of subgroup i in subarea j
              Riskjj         =     cancer risk for subgroup i in subarea j
              n            =     number of subgroups
              m            =     number of subareas

              The calculated population cancer risk represents the hypothetical number of
       additional cancer cases within the study area due to stack emissions at the WTI
       facility, given the assumptions inherent in the calculation of individual risk.

C.     Overview of Individual Risks Associated with Stack Gas Emissions
       Using the methodologies described above, excess cancer risks and HQ values are
estimated for the following major population subgroups:

       •      Adult non-farming resident;
       •      Child non-farming resident;
       •      Adult farmer; and
       •      Child of farmer.

       In addition to these major subgroups, which are expected to comprise a significant
portion of the local population, three subgroups of the population,  which may experience
elevated exposures  due to their particular behavior patterns also identified:

       •      School-age child resident;
       •      Adult subsistence farmer; and
       •      Child of subsistence farmer.

       For each of the two sets of subgroups listed above, inhalation cancer risks and
noncancer HQ values are estimated for more than 200 substances of potential concern in each
of the 12 subareas.  For the indirect pathways of exposure, excess cancer risks and
noncancer HQ values are estimated for the 45 subs^nces of primary ccmcem,  which include
metals, dioxin/furan congeners, organic chemical residues and PICs with the greatest
potential to accumulate in the food chain.
-------
       The risks associated with direct and indirect exposure by the seven population
subgroups are discussed below.  To represent potential variations of risks within subareas, two
"risk descriptors" are calculated based on the average and maximum doses calculated for each
subarea.  As indicated in Chapter VII, the average dose is calculated based on the average
estimated concentration within a subarea, and the maximum dose is calculated based on the
maximum concentration within a subarea. Each of these two risk descriptors is based on
average emission rates and average exposure factors.  However, average dose is estimated
based on the average air concentration within a subarea, and the maximum dose is estimated
based on the maximum air concentration within a subarea.
       To evaluate the effects of potential variations in emission rates and exposure factors on
estimated risks, a sensitivity analysis was conducted.  This sensitivity  analysis looks at the
variability in exposure for two "high-end" subgroups. The methodology used in the sensitivity
analysis is described in a separate section later in this  chapter. Table VIII-2 summarizes  the
components used to estimate risk for the two risk descriptors (described above) and the high-
end subgroups evaluated in the sensitivity analysis.
       Results are also presented for an analysis of the potential effects of lead emissions from
the incinerator, and the risks posed by the four activities identified below as  potentially leading
to higher exposures (i.e.,  ingestion of fish by a subsistence fisherman, ingestion of deer hunted
locally, consumption of mother's milk by an infant, and consumption of homegrown
vegetables).
       In addition to the subgroups identified above, excess cancer risks and noncancer HQ
values are estimated for the following four activities that may lead  to significantly higher
exposures, but in which only a relatively small fraction of the population is expected to
participate:

       •      Consumption of locally caught fish by a subsistence fisherman;
       •      Consumption of deer harvested locally  by hunters;
       •      Consumption of mother's milk by breast-feeding infants; and
       •      Consumption of homegrown fruits and  vegetables from residential gardens.

For some individuals,  the risks estimated for these specific activities could be an incremental
addition to the pathways described earlier.  It should also be noted that risks associated with
mother's milk is estimated for residents, farmers, and subsistence farmers.

       1.     Individual Risks Due to Direct (Inhalation) Exposure ,.
              For the inhalation pathway, excess cancer risks and noncancer HQ values  are
       estimated for the substances of potential concern for stack gas  emissions, including
 Volume V                                VIE-6
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        organic compounds and PICs, dioxin and furan congeners, metals, and hydrochloric
        acid (HC1).  Nitrogen oxides (NOJ, sulfur oxides (SOJ, and particles are examined
        by comparison to the National Ambient Air Quality Standards (NAAQS). Cancer
        risks and noncancer HQ values for the inhalation pathway are estimated based on: 1)
        the average vapor concentration calculated within each subarea; and 2) the maximum
        calculated vapor concentration in each subarea.

              a.     Carcinogenic Effects
                     Table Vm-3 summarizes the estimated total inhalation cancer  risks for
              the substances of potential concern for each subarea. Area average inhalation
              cancer risks  are based on average air concentrations estimated  in each subarea.
              as described in Chapter VII.  In addition, excess cancer risks at the point of
              maximum vapor concentration in each  subarea are also presented. As shown
              in Table Vin-3, estimated average cancer risks do not exceed 1 x 10"7 for any
              population subgroup in any subarea.  The highest inhalation cancer risk,
              8 x 10'8, (assuming average concentrations) is for children of residents and
              fanners living in subarea El.  Inhalation cancer risks in subarea Wl are
              approximately 30 percent lower than estimated average risks in subarea El.
              Average cancer risks in subareas SI and Nl for all subgroups are
              approximately half those estimated in subarea El.
                    As evident from Table Vffl-3, cancer risks tend to decrease with
              increasing distance from the facility.  In general, risks decrease by a factor of
              2  to 3 from subarea to subarea as the distance from the site increases  in any
              one direction (e.g., El to E2  or E2 to E3).
                    Cancer risks estimated at the point of maximum concentration follow a
              similar pattern to that described above,  but are generally a factor of 2 to 4
              higher than estimated average cancer risks.  The highest estimated cancer risk,
              2 x 10'7, is for children of residents and farmers living in subarea El at the
              point of maximum concentration.  Appendix V-14 presents the inhalation
              cancer risks for individual substances of potential concern.

              b.     Noncarcinogenic Effects
                    Table Vm-4 summarizes HI values estimated for the substances of
              potential concern, based on the estimated air concentrations in each subarea.
              As shown in Table VHI-4, estimated total HI values do*not exceed 1.0 (unity),
              indicating that adverse noncancer human health effects are not expected to
              occur due to inhalation exposure.  Similar to the pattern of average cancer

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             risks described above, the potential for noncancer health effects is greatest in
             subarea El followed by subarea Wl.  ffl values in other subareas are
             significantly lower than values estimated for subarea El, and tend to decrease
             with increasing distance from the facility.  HI values are highest for children
             of residents and farmers, but do not exceed 5 x 10"2 based on average
             concentrations within subarea El.
                    HI values are estimated to be 2 to 4 times higher at the point of
             maximum concentration than HI values based on the areal average
             concentration.  HI values for children  of residents and farmers  in subarea El
             are 1 x 10"1 based on maximum estimated concentrations in subarea El.  HI
             values  in other subareas based on maximum estimated concentrations do not
             exceed 1 x ICr1 for any subgroup.  Appendix V-14 contains inhalation HQ
             values  for the substances of potential concern considered in this assessment.

             c.     Potential Health Effects Associated with Inhalation of NOX, SOX,
                    and Particulate Matter
                    Chronic toxicity criteria  have not been established by U.S. EPA for
             SOT, NOT, or particles less than 10 microns in diameter (PMIO). Thus, an
             evaluation of the risks posed by emissions of these substances is performed by
             comparison to annual average National Ambient Air Quality Standards
             (NAAQS).  U.S. EPA has developed annual average NAAQS values for NO:,
             SO2, and PM10 of 100,  80,  and 50 fj.g/m3, respectively. The maximum and
             average ground-level air concentrations of these substances estimated in each
             subarea are presented in Table VHI-5.   As shown in Table Vffl-5, the average
             predicted concentrations of SO,, NO,,  and PMIO in the subareas are at least
             100 times less than the NAAQS, with  maximum predicted concentrations at
             least a  factor of 10 below the NAAQS in all subareas. The highest estimated
             concentrations of SO,, NO,, and PM10 within a single subarea are predicted to
             occur in subarea El. Using the NAAQS as a guideline, inhalation exposure to
             SO,, NOX, and PM10 emissions from the WTI facility stack is, therefore, not
             expected to pose a significant health risk.

      2.     Risks Due to Indirect Exposure
             For the indirect routes of exposure, average and maximum excess cancer risks
      and noncancer HQ values are estimated for the dioxin/furan congeners, metals, and
      other surrogate organic chemicals.  Average risk estimates are based on average
      emission rates, average dispersion/deposition  within a subarea, and typical  exposure
Volume V
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       factors.  Maximum risks are also estimated using average emission rates and typical
       exposure factors, but are estimated at the point of maximum vapor concentration
       (based on air dispersion modeling) within a subarea.
              As described in Chapter IV, a screening process was developed to identify the
       organic residues and PICs  that represent the greatest potential health hazard through
       the indirect exposure pathways. For each of the surrogate chemicals identified to be
       of primary concern (including dioxin/furan congeners, metals, and organic residues
       and PICs), cancer risks and/or noncancer HQs are estimated for the following
       exposure pathways:

              •     Soil ingestion;
              •     Dermal  contact with soil;
              •     Consumption of meat (beef, pork, and poultry) and eggs from locally
                    raised livestock;
              •     Consumption of milk and dairy products (cheese, milk desserts, yogurt,
                    cream, and butter) from locally raised cows;
              •     Consumption of homegrown fruits and vegetables;
              •     Ingestion of  river/lake water during swimming; and
              •     Dermal contact with river/lake water during swimming.

       The pathways of exposure applicable to the individual subgroups were identified
       earlier in Table V-l.
             Tables Vm-6 and VTJJ-7 summarize the estimated total cancer risks and
       noncancer hazard indices for the seven population subgroups in the subareas
       designated. The average cancer risks and hazard indices are based on media
       concentrations estimated from average emission rates and average contaminant
       deposition within each subarea. Cancer risks and HI values  for the location of
       maximum exposure in each subarea are also presented in Tables Vm-6 and VDI-7.
       Estimated cancer risks do not exceed 1  x  10"3 for any population subgroup.  Estimated
       HI values are at least an order of magnitude below unity for exposure under both
       average and maximum concentration conditions. As shown in Tables VTfl-6 and
       VUJ-7,  the subsistence fanner and child population subgroups have the highest cancer
       risk and HI values. In subarea El, where the highest risks are predicted, cancer risks
       to the subsistence farmer and child are  1 x 10* (for both subgroups), based on
       average concentrations within the subarea. Average cancer risks for other subgroups
       do not exceed  5 x 10~7.  Cancer risks at the location of maximum concentration in
       subarea El are estimated to be 4 x 10"* for the subsistence farmer and child, and risks

Volume V                              VTTT-Q
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       are generally 2 to 3 times greater than the average estimated risks.  Cancer risks do
       not exceed 2 x 10"6 for the resident, farmer, and school child subgroups.
              HI values are also estimated to be highest in subarea El, with subarea Wl
       somewhat lower (approximately 30 percent).  HI values in subarea El based on
       average and  maximum concentrations do not exceed 2 x 10": and 5 x 10:,
       respectively, for the child of a subsistence farmer.  For other subgroups, estimated HI
       values, based on average and maximum concentrations, do not  exceed 8 x  10"3 and 2
       x 10"2, respectively.  Appendix V-15 contains cancer risks and HQ values for the
       individual substances of primary concern estimated for the indirect exposure pathways
       that are considered in this assessment.2
              Tables Vni-8 and Vffl-9 provide risk estimates for individual exposure
       pathways for the subsistence farmer (exposure pathway-specific cancer risks and HI
       values for the other population subgroups are provided in Appendix V-16).   As Tables
       VrH-8 and Vin-9 show,  consumption of food (i.e., ingestion of meat and eggs from
       locally raised livestock, consumption of milk and dairy products from locally raised
       cows, and consumption of homegrown fruits and vegetables) is  the most significant
       exposure pathway for the subsistence fanner.  The distribution of risks between the
       various food pathways varies somewhat between subgroups, due to varying
       consumption rates between subgroups (e.g., dairy products consumption accounts for
       a greater proportion of the total risk for children than for adults due to significantly
       higher milk consumption rates in children), as shown in Appendix V-16.  Risks from
       non-food exposure pathways (soil and surface water related pathways), however, are
       relatively insignificant.
             Tables Vni-10 and VHI-11  present  chemical-specific cancer risks and
       noncancer HQ values for the adult subsistence farmer in subarea El.  The most
       important contributors to total cancer risk are the dioxin and furans congeners
       (accounting for 76 percent of the total cancer risk for the subsistence farmer in
       subarea El).   In particular, 2,3,4,7,8-pentachlorodibenzofuran (2,3,4,7,8-PeCDF)
    2 As noted in Chapter VH, upon estimation of the cancer risks and noncancer HI values,
an adjustment to the study area boundary would be made if it appeared that the boundary of
the preliminarily defined study area did not include all areas of potentially significant risk.
However,  as apparent from  a review of the cumulative human health risks estimated in the
subareas on the outer ring of the study area (i.e., subareas E3,  S3, W3, and N3), the area            ^
outside the designated study area is expected to be very low risk (i.e., less than a 1  x 107
cancer risk or His less than 0.1) for all population subgroups.  The study area and the
subareas within the study area, as defined in Chapter VH, therefore, are assumed to include
all areas of significant risk.

Volume V                              \rrrr in
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       accounts for 38 percent of the cancer risk for a subsistence fanner in subarea El.
       Organic compounds account for the greatest portion of the total HI (71 percent) with
       hexachlorophene accounting for approximately 45 percent of the total HI value.  The
       metals with the greatest contribution to the total HI are thallium and  mercury.
       together accounting for over 90 percent of the total HI for inorganic  compounds, and
       16 and 15 percent, respectively, of the total HI for all compounds.
              Tables Vm-12 and VHI-13 present  the combined direct and indirect cancer
       risks (sum of values in Tables Vm-3 and VTH-6) and HI values (sum of values in
       Tables Vm-4 and Vm-7), respectively.  Total cancer risks and HI values are greatest
       in subarea El, with the highest risk experienced by adult subsistence farmers and
       children of subsistence farmers.

       3.     Sensitivity Analysis of Exposure Parameters for the Highly Exposed
              Subgroups
              Exposure parameters (e.g., ingestion rate, inhalation rate, exposure frequency)
       are used in the exposure assessment process to reflect the behavior and activity
       patterns of the population subgroups.   The  values of these exposure parameters are
       often based on the assumption that the exposed population or subgroup  is
       homogeneous.  In reality, however, the exposed population actually consists of many
       individuals, with a distribution of exposures due to varying inhalation rates, ingestion
       rates,  exposure durations and other critical  behavioral characteristics.
              To evaluate the variability in risks estimated for the most highly exposed
       subgroups, the subsistence farmer and  child in subarea El  (as noted above), the
       exposure parameters (in Appendix V-8) that have the most significant impact on the
       magnitude of potential exposures are identified and varied to determine  "high-end"
       risks.  These parameters are identified by setting each parameter, in turn, at the high-
       end value and calculating the resulting risks.  The two parameters that result  in the
       greatest increase in exposure (and risk) are identified for each exposure pathway.
       Using the identified parameters, high-end exposure and the associated risk are
       estimated.
              For example, for food consumption  pathways, assuming that the body weight
       and lifetime are constants, the lifetime average daily dose through each  food pathway
       is estimated varying each of the following parameters:
                                                               t*
              CM:   Chemical Concentration in Food (related to emission rate)
             IR:   Food Ingestion Rate
              FI:   Fraction Ingested from Contaminated Source

Volume V                               inrr 11
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              EF:   Exposure Frequency
              ED:   Exposure Duration

       For the adult subsistence farmer, the exposure parameters with the greatest effect on
       total risk are food ingestion rates and exposure duration.  For the subsistence fanner
       child, the exposure parameters with the greatest effect on total risk are food ingestion
       rates and concentration in food (estimated based on the variability in the emission
       rates).  Risks are thus re-calculated with these parameters set at the high-end value
       and all the other parameters set at their typical values. The resulting risk estimates
       represent the upper end of the risk distribution for the adult and child subsistence
       fanner exposure population subgroups in subarea El ,  the most highly exposed
       subgroups in the general population.
              As shown in Tables Vin-14 and VUI-15, high-end food consumption cancer
       risks and hazard indices for the subsistence fanner and child are generally 2 to 6
       times higher than average cancer risks and hazard indices.  Total high-end cancer risk
       (all exposure pathways combined)  for the subsistence fanner and child do not exceed
       7 x 10"*, and the cumulative high-end noncancer hazard indices are 1 x 10"1 for the
       subsistence farmer child and 2 x 10"2 for the subsistence farmer. Appendix V-17
       provides details of the high-end cancer risks and hazard indices estimated for the
       subsistence farmer and child in subarea El.

       4.    Estimation of the Potential Health Effects Due to Lead
             The evaluation  of risks associated with exposure to lead requires the use of
       U.S.  EPA's Integrated Exposure Uptake Biokinetic (IEUBK) model for lead in
       children,  a computerized model that predicts blood lead concentrations in children
       exposed to lead  through a variety of media.  The model is designed to estimate blood
       lead levels using a combination of default exposure assumptions and site-specific
       exposure information,  where available.
             The assessment of risks associated with exposure to lead from the WTI facility
       is conducted  using version 0.99d of the IEUBK model, which is calibrated for
       children from one-half to seven years of age (U.S. EPA 1994e). Uptake of lead  from
       five media (air,  drinking water, soil/dust, food, and paint) is evaluated by the model.
       For this assessment, blood lead levels for children in the one to seven year-old age
       range are modeled.
                                                                  y*
             The default input values used in the IEUBK model  are presented in Table  VIH-
       16.  Two site-specific  exposure values (background lead concentrations in air and
       child  inhalation  rates) are substituted for the model default values for the WTI site
Volume V
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       analysis.  The default air lead concentration of 0.1 ^g/m3 is replaced with an
       estimated background air lead concentration of 0.065 fig/m3 (OEPA 1993).  This
       concentration is estimated from air sampling conducted at the East Elementary School
       in East Liverpool, which was compiled by Ohio EPA.  Monthly samples were
       collected from this monitoring station during late-1992 and early 1993, prior to full
       operation of the WTI facility.  None of the samples indicated the presence of lead in
       air above the detection limit (which ranged from 0.075 to 0.188 ng/m3).  The lead
       concentration in air is estimated as the average of one-half the detection  limits for the
       seven monthly samples.
             In addition, the default age-specific inhalation rates for one to.seven year-old
       children, which  ranged from 2 to 7 m3/day, are changed to 16 mVday for all ages to
       be consistent with the inhalation rate for children used elsewhere in this  risk
       assessment.  This change likely results in an overestimate of the potential for adverse
       health effects in children due to inhalation of lead.
             For all media modeled, site-specific incremental increases in lead
       concentrations attributed to the WTI incinerator are added to the default  values or
       site-specific background lead concentrations. In all cases,  however, the  magnitude of
       these incremental increases is too small to change the model inputs (i.e., modeled
       media lead concentrations due to the WTI facility are insignificant compared to
       estimated background levels of lead in the environment).
             According to U.S.  EPA, the Food and  Drug Administration (FDA),  the
       Centers for Disease Control (CDC), and other regulatory bodies, low-level exposure
       to lead during infancy and childhood increases the risk of irreversible neurobehavioral
       deficits at levels of internal exposure as low as 10 ng/dL (CDC 1991; U.S.  EPA
       1990c, 1994e; USDHHS 1990; ATSDR 1993). In general, regulatory agencies
       consider exposures that correspond to blood lead levels of 10  /zg/dL or less  in 95
       percent of exposed children to be acceptable.  The Guidance Manual for the IEUBK
       model (version 0.99d) for lead in children (U.S.  EPA 1994e)  states:

             "At present the definition of elevated blood lead (EBL) is the level of
             concern of 10 pg/dL defined by U.S. EPA (1990g) as  the lower limit
             of the range of known possible adverse neurobehavioral effects in
             young children.  The protection level most often used in practice  is a
             maximum 5 percent risk of elevated blood lead (EBL)  for children in a
             given household."
                                                                +*
       This criterion is  used in the WTI incinerator site analysis.
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              The output of the EEUBK model is a probability curve constructed around a
       modeled geometric mean blood lead concentration. From this probability curve, the
       95th percentile of the children's blood lead concentrations can be determined.  The
       probability curve from the WTI incinerator site analysis is shown in Figure VHI-1.
       As is demonstrated by this probability curve, over 98% of the children who may be
       exposed to lead in the environment from both background sources and from the WTI
       facility are predicted to have blood lead levels below the 10 jig/dL level.  It should be
       noted that this percentage of children below 10 /tg/dL remains unchanged whether or
       not the emissions from the WTI facility are considered, since  exposures to
       background levels of lead in air and soil far exceed exposures specifically associated
       with operation of the WTI facility.  This observation indicates that lead emissions
       from the incinerator stack should have no adverse impacts on  local children and
       would not change the estimated number of local children with elevated blood lead
       levels.
              Because one to seven-year-old children are generally considered more sensitive
       to lead exposure that older children or adults, further analysis  of lead exposure and
       potential health effects is not conducted.

       5.     Risks Associated with Specific Activities
              As noted earlier, a limited number of individuals in the population may be
       engaged in specific activities that may result in elevated risks (e.g., subsistence
       fishing, deer hunting, home gardening, and consumption of mother's milk by an
       infant).  For some individuals, the risks estimated for these specific activities could be
       an incremental addition to the risks  associated with the exposure pathways described
       earlier.  Risks associated with the substances of primary concern (including
       dioxin/furans, surrogate organic chemicals, and metals) through the indirect exposure
       pathways are estimated for the populations described below.

             a.     Subsistence Fishing
                    As indicated in Chapter vn, an analysis of local fishing data indicate
             that consumption of locally caught fish by the general residential population is
             unlikely to be a significant source of exposures.  However, it is possible that a
             subgroup of the population may derive a significant portion of their daily diet
             from locally  caught fish (subsistence fishing). Cancer risks and noncancer
             HQs are estimated for subsistence fishing based on the  estimated dose via fish
             ingestion for the substances of primary concern.  Table Vni-17 summarizes
             the total cancer risks and hazard indices for each of the subareas.  Average
Volume V
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              risks are estimated based on average dispersion and deposition of contaminants
              within a subarea. Chemical-specific cancer risks and HQ values are shown in
              Appendix V-18.
                     In estimating cancer risks and noncancer HQs for subsistence fishing.
              actual bodies of water in the vicinity of the WTI facility in which fishing
              reportedly occurs are identified. Segments of the Ohio River (the largest body
              of water in the vicinity of the facility and the one most frequently used for
              fishing) are evaluated in each of the subareas through which it passes.  In
              addition, Little Beaver Creek, which is located in Ohio near the Ohio-
              Pennsylvania border (subarea N2), is evaluated because discussions  with local
              wildlife officials indicated that this body of water is a popular fishing location.
              Finally, Tomlinson Run Lake, located approximately 6 miles south of the WTI
              facility in West Virginia is also evaluated to include a lake environment (i.e,
              the other water bodies are rivers or creeks). Tomlinson Run Lake is located
              in subarea S3.
                     As shown in Table VQI-17, subsistence consumption of fish from
              recreational areas located in the vicinity of the WTI facility results in
              incremental cancer risks of less than 6 x 10~8, with the highest risks  due to
              fishing in the Ohio River.   HI values are estimated to be significantly less than
              1.0 for all subareas where lakes or rivers are located.  Estimated HI values
              based on average concentrations do not exceed 4 x 1CT3 (Tomlinson Run Lake).
              Maximum concentration HI values are not estimated for Tomlinson Run Lake
              because it is located several miles from the point of maximum concentration.
              The estimated HI value for subsistence fishing in the Ohio River at the
              location of maximum concentration is estimated to be 2 x 10"3.
                    It should be noted that in the assessment,  it is assumed that mercury in
              aquatic environments is found as both inorganic mercury and methylmercury,
              which fate and transport modeling indicates  will bioaccumulate to a greater
              degree than inorganic  mercury.  As noted in Chapter VI, 25 percent of the
              mercury in aquatic environments is estimated to be in the form of
              methylmercury.  Chemical-specific  risks associated with aquatic exposure  to
              inorganic mercury and methylmercury are tabulated in Appendix V-18.
                    Due to the relatively insignificant risks associated with subsistence
              fishing, total risks would not increase significantly for individuals participating
              in this activity.
Volume V
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              b.    Deer Hunting
                    Deer living in the vicinity of the WTI facility may be exposed to
              contaminants released from the WTI facility stack.  It is possible, therefore.
              that individuals hunting in the area surrounding the WTI facility and
              consuming deer meat may be indirectly exposed to substances released from
              the WTI facility stack.
                    Deer meat concentrations are estimated in  a fashion  similar to that used
              for beef concentrations, assuming the same biotransfer and bioconcentration
              factors as for beef but using dry matter consumption rates and fat contents that
              are specific for deer.  Excess cancer risks and noncancer HQs are estimated
              for the consumption of meat from deer hunted in the vicinity of the WTI
              facility.  Table VIE-18 summarizes the total cancer  risks  and hazard indices
              for each of the subareas. Average risks are estimated based on average
              dispersion and  deposition of contaminants within a subarea.   In addition.
              cancer risks and hazard indices at the point of maximum concentration within a
              subarea are also evaluated,  and are presented in Table V1H-18.  As shown in
              Table VTQ-18,  the incremental average cancer risks  do not exceed  1 x 10~8,
              and average HI values do not exceed 5 x 10"5, for all subareas.  Maximum
              cancer risks and HI values are generally 2 to 3 times higher than average
              estimated risks.  The  highest cancer risks and HI values for consumption of
              deer meat occur in subarea El.  Cancer risks and  HI values  in subareas Wl,
              SI, and Nl  are somewhat lower (approximately 30 to  70 percent lower).  It
              should be noted, however, that it is unlikely that significant deer hunting
              occurs in the subareas immediately surrounding the WTI facility due to the
              proximity of developed areas.  Farther away from the  facility, where  hunting
              is more likely,  risks tend to decrease by a factor of 2 to 3 (from subarea to
              subarea) as the distance  increases from the WTI facility.   Chemical-specific
              cancer risks and HQ values are shown in Appendix V-18.

              c.     Home Gardening
                    Some residents living in East Liverpool and surrounding areas have
              home gardens from which they may consume fruits and vegetables. An
              informal home  gardening survey was conducted in June 1993 by the East
              Liverpool Board of Health, as described in Chapter VIL,  As a result of this
              survey, the Board  of Health estimated that approximately  30 percent of local
              residents have home gardens.  Therefore, excess cancer risks and noncancer
              HQs due to exposure  to stack gas constituents deposited on and accumulated in
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                         homegrown fruits and vegetables are estimated for this segment of the
                         population.
                               Table Vm-19 summarizes the total cancer risks and HI values for each
                         of the subareas.  Average cancer risks and noncancer HI values are estimated
                         based on average dispersion and deposition of contaminants within a subarea.
                         In addition, cancer risks and noncancer HI values  at the point of maximum
                         concentration within a subarea are also evaluated,  as shown in Table VTH-19.
                         Average cancer risks for ingestion of homegrown vegetables by residents with
                         gardens are below 6 x 10~9 for all subareas and the hazard indices  do not
                         exceed 1 x 1CF*.  Cancer risks and hazard indices at the location of maximum
                         concentration in each of the subareas are 2 to 3 times higher than the  average
                         cancer risks and hazard indices.
                               It should be noted that this assessment is limited to the consideration of
                         fruits and vegetables from home gardens and does not consider the
                         consumption of locally raised produce by individuals without home gardens.
                         However, due to the low level of risk estimated, it is unlikely that locally
/                        grown vegetables pose a significant health risk. In addition, due to the
v ^                     relatively insignificant cancer risks and HI values estimated for home
                         gardening, risks associated with this activity will not appreciably increase total
                         risks to local residents.

                         d.     Ingestion of Mother's Milk by Infant
                               Lipophilic compounds, such  as dioxins and furans, may accumulate in
                         body tissues and preferentially concentrate in adipose tissue.  Exposure to
                         these compounds by a mother before and while lactating, therefore, may result
                         in the accumulation of contaminants in  breast milk, and exposures  to breast-
                         feeding infants during nursing.
                               Excess cancer risks are estimated  for infants exposed to contaminants
                        accumulated in  mother's milk.  In calculating exposure levels for the infant
                        through breast milk ingestion,  it is assumed that the mother receives exposure
                        through each of the pathways considered  for a particular subgroup.  Table
                        Vin-20 summarizes the total cancer risks for each of the  subareas.  Average
                        cancer risks are estimated based on average dispersion and deposition of
                        contaminants within a subarea.  In addition, cancer risks at the point of
/""-                        .                                              '•
v                        maximum concentration within a subarea are also evaluated,  as shown in Table
                        vm-20.  It should be noted that noncancer health effects  due to infant
                        ingestion of breast milk are not considered in this assessment due to the
          Volume V
                                                   \7TTT  1 "I
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              significant uncertainty in applying noncancer toxicity data to infants (U.S.
              EPA 1994a).
                    Cancer risks based on average subarea exposures  do not exceed 4x10
              for infants of residents, 7 x 10"7 for children of fanners, and 2 x 106 for
              children of subsistence farmers. These cancer risks are estimated for subarea
              El;  the subarea with the next highest average cancer risks is subarea Wl,
              where estimated risks are approximately 30 percent lower than in subarea El.
              The primary contributor to the  estimated average cancer risk of the infant of a
              subsistence farmer in subarea El are the non-dioxin organic compounds (66
              percent of total risk) with benzo(a)pyrene accounting for  37 percent of the total
              average cancer risk. Dioxin and furan congeners as a whole account for 34
              percent of the total estimated average cancer risk.  Chemical-specific cancer
              risks for the infant of a subsistence farmer in subarea El  are provided in
              Appendix V-15.
                    Cancer risks estimated for the point of maximum concentration in each
              subarea are generally 2 to 3 times higher than the average risks.  Estimated
              maximum location cancer risks  for breast-feeding infants  of non-farming
              residents are 1 x 10"6 in subarea El,  the area of greatest impact, while breast-
              feeding infants of fanners and subsistence fanners are 2 x 10* and 5 x  10"6,
              respectively,  in subarea El.

D.     Overview of Population Risks
       Individual risks are estimated for several population subgroups in the 12 subareas
surrounding the WTI facility.  These individual risks  are combined with population data for
each subarea (and subgroup) to estimate the cancer risk burden for the population within the
study area. The population cancer risk is calculated as the individual cancer risk for each
member of a population subgroup multiplied by the number of individuals in that population
subgroup, summed across all subgroups.
       Population data for ZIP codes contained partially or wholly within the study area have
been compiled (CACI 1991). The population  within three age groups—infants (0 to 12
months), children (1 to 12 years), and adults (13 years and older)—is estimated for each ZIP
code area, and the fraction of each ZIP code area contained within each subarea is estimated
based on Figure VIII-2.  Appendix V-19 summarizes  the population data for each ZIP code
and the fraction of each ZIP code contained within  each risk assessment subarea.  The
product of the fraction of a ZIP code area contained within a subarea and the ZIP code area
population is used to estimate subarea populations.  This methodology assumes that the
population within a ZIP code area is evenly distributed; therefore,  the population  within

Volume V                              -~— •-
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 some subareas may be underestimated while the population in others it may be
 overestimated. This uncertainty, however, is not expected to impact significantly the results
 of the population risk assessment.
       The total population is divided into the farming and the non-farming population.
 Census data on the farming population in the area surrounding the WTI facility were not
 readily  available; therefore, the farming population is estimated.  As indicated in Chapter
 VH, the 1992 Agricultural Census (USDC 1993a,b,c) identifies the number of farms in each
 of the three counties (Columbiana, Ohio; Beaver, Pennsylvania; and Hancock, West
 Virginia).  The fraction of the total population associated with farms is estimated using the
 data presented in Table VTI-13.  As a result, the farming population is estimated to comprise
 approximately 2.4 percent, 0.7 percent, and 0.5 percent,  of the total populations of
 Columbiana, Beaver, and Hancock counties, respectively. These values are estimated based
 on the average number of individuals per household (as indicated in Table VII-13), which
 may underestimate typical farming households.  Thus, to ensure that  the fanning population
 is not underestimated, it is assumed that the farming population in the vicinity of the WTI
 facility comprises approximately 2.5 percent of the total population (the upper end of the
 values for the local counties).  This method may underestimate the farming population in
 some subareas (likely those outside the East  Liverpool area, i.e., farther from the facility)
 and overestimate the farming population in others (i.e., those near the facility in the more
 urbanized areas).   The  remaining 97.5 percent of the population is assumed to be non-
 farming residents.  Furthermore, as indicated in Chapter VII,  30 percent of the non-farming
 population  are assumed  to have home gardens.  Based on these assumptions, the total
 estimated farming  and non-farming populations  within each subarea is estimated, as shown  in
 Table Vm-21.
       Direct  and indirect cancer risks are summed for the farming and non-farming
population  subgroups, as shown in Table Vin-22. For the residents with  home gardens,
 risks associated with consumption of homegrown fruits and vegetables (Table VUI-19) are
added to the indirect risks from other pathways and direct risks to develop the total risk
estimates in Table Vin-22. Total average  cancer  risks for each population subgroup are
multiplied by the corresponding age-distributed  census data for each  subarea to estimate the
estimated number of additional cancer cases due to facility stack emissions (Table VTQ-23)
for each subgroup  in each subarea.  It should be noted that cancer risks estimated for
children (1 to  6 years old) are applied to the entire age range of children (1 to 12 years) in
estimating population risk,  with the exception of indirect risks to infants for which risks from
                                                                 •?'*
breast milk consumption are applied. In addition, inhalation risks estimated for children are
applied to infants.
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       Table Vffl-23 shows the population risk burden for the farming and non-farming
 subgroups for each subarea.  The population cancer burden for the WTI study area is
 estimated as 3 x 10"3, which implies that over a 70 year lifetime, including 30 years of WTI
 operation, 0.003 cancer cases are estimated to occur due to impacts from stack emissions.
 As a basis for comparison, statistics from the American Cancer Society (1993) indicate that
 the incidence of cancer from all sources is approximately  33 percent.   Given the total
 population of approximately 54,000 individuals in the study area, this "background" cancer
 risk without operation of the WTI facility corresponds to approximately 18,000 cancer cases
 over a lifetime.

 £.    Estimation of Risks Due to Fugitive Emissions
       As discussed in Volume IE, several sources of fugitive organic vapor emissions
 associated with waste handling, processing, and storage prior to combustion, are identified at
 the WTI facility, including:

       1)    Carbon adsorption bed (CAB) system, which controls emissions from tanks in
             the organic waste tank farm building and from the container processing area;
       2)    Seals, valves, and flanges associated with tanks  in the organic waste tank farm
             building;
       3)    Waste water holding tank;
       4)    On-site truck wash station; and
       5)    Ash handling.

       Exposure to emissions from  these sources may occur to individuals living, working,
or attending school in the vicinity of the WTI facility.  Given the nature of the fugitive vapor
releases and the  extent of atmospheric dispersion predicted, only risks through inhalation are
quantified for organic vapor emissions from sources  1 through  4.  For fugitive ash emissions
(source 5), direct and indirect exposure  pathways are evaluated.  Risks associated with these
exposures are estimated for three potential exposure populations: adult residents, child
residents, and school-age children.
       Exposures are estimated in four quadrants (north, south, east, and west of the facility)
that extend to a distance of 2,000 feet from the facility stack and include  residential and
commercial areas of East Liverpool and the East Elementary School to the north of the
facility.  For the fugitive organic vapor  emissions sources  (1 through 4 above), inhalation
cancer risks and HQ values are estimated for the 11  surrogate organic compounds identified
in Chapter IV.  For the  fugitive ash source (source 5), direct and indirect cancer risks and
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 HQ values are estimated for the metals identified in the ash in Chapter IV.  The following
 sections summarize the estimated risks for these sources.

        1.     Estimated Risks Due to Fugitive Organic Vapor Emissions
              Inhalation cancer risks and noncancer HQs are estimated within each of the
        four quadrants shown in Figure VII-4 for 11 surrogate organic chemicals that were
        selected for evaluation in Chapter IV.  Total cancer risks and hazard indices for the
        four sources of fugitive emissions identified at the facility combined are presented in
        Table VHI-24, based on average vapor concentrations.  As indicated in Table Vm-24.
        lifetime cancer risks due to average exposure to fugitive emissions from the WTI
        facility (all four sources of identified fugitive organic vapor emissions sources
        combined) are below 5 x 10* for children (1 to 6 years old) and school-age children
        (7 to 12 years old) and below 1 x 10"6 for adults.  Total noncancer hazard indices are
        estimated to be significantly below 1, with a maximum estimated hazard index of 7 x
        102 for children (1 to 6 years old) who spend most of their time in the areas east and
       west of the facility.
              In addition to average risks associated  with fugitive releases from the WTI
       facility, excess cancer risks and noncancer HQs are estimated at the point of off-site
       maximum concentration for each of the four fugitive emissions sources.  Total cancer
       risks and hazard indices for the 11 surrogate chemicals combined are presented in
       Table VHI-25.  Cancer risks and HI values for individual substances are presented in
       Appendix V-20.  It should be noted that the location of maximum  concentration for
       all sources except the elevated CAB source are on-site, thus the maximum off-site
       concentrations at receptors located along the fenceline are used in the analysis. Since
       residences near the site are generally between 1,000 and 1,500 feet from the
       fenceline, the estimation of long-term inhalation risks at the location of maximum
       concentration (i.e., based on exposure for 24 hours/day,  350 days/yr, and up to 9
       years) is unrealistic and represents worst-case exposure.  Nonetheless, cancer risks for
       the four organic vapor fugitive emissions sources identified at the WTI facility are
       below 1 x 10"5 at the respective locations of maximum concentration.  The noncancer
       hazard indices for each of the four fugitive organic vapor sources are below 1.0,
       indicating that adverse noncancer  health effects due to inhalation exposure are unlikely
       to result from activities at the WTI facility.

       2.    Risks Due to Fugitive Ash Emissions
             Fugitive ash emissions from the loading of trucks is expected to occur as part
       of routine operations at the WTI facility.  Average inhalation cancer risks and

Volume V                               VTTT_TI
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       noncancer HQs are estimated within each of the four quadrants shown in Figure VII-
       4, for metals and cyanide that have been detected in samples of ash from the ESP at
       the facility.  In addition, because deposition of fugitive ash emissions may  occur in
       the vicinity of the WTI facility, cancer risks and noncancer HQ values are estimated
       for several indirect pathways, including ingestion of and dermal contact with soil,  and
       consumption of homegrown vegetables.  Indirect risks and HQ values are estimated
       for adult and child residents and school  children who may be exposed by these
       pathways.
              Total inhalation cancer risks and hazard indices, based on average airborne
       concentrations of ash off-site, are presented in Table Vin-26.  Cancer risks and HQ
       values for individual substances are presented in Appendix V-20.  As indicated in
       Table VIH-26, lifetime cancer risks due to average inhalation exposure to fugitive  ash
       emissions from the WTI facility are beiow 5 x 10"8 for children (1 to 6 years old) and
       less than 3 x  10~8 for school-age children (7 to 12  years old).  For adults, the
       estimated average cancer risks do not exceed 2 x 10~8. The highest cancer  risks are
       predicted for the area west  of the site.  Noncancer HI values are estimated to be
       significantly below 1.0 in all quadrants;  the highest average HI value of 7 x 10^ is
       estimated for the area west  of the facility for children (1 to 6 years old).
             In addition to average risks, cancer risks and noncancer HQs are estimated  at
       the point of maximum off-site concentration of fugitive ash. Total inhalation cancer
       risks and hazard indices are presented in Table VH3-26.  It should be noted that the
       location of maximum concentration is on-site, thus the maximum off-site
       concentration at a receptor located along the fenceline is used in the analysis.  Since
       residences near the site are  generally between 1,000 and 1,500 feet from the
       fenceline, the estimation of  long-term inhalation risks at this location of maximum
       concentration (i.e., based on exposure for 24 hours/day,  350 days/yr) is unrealistic
       and represents worst-case exposure. Nonetheless,  cancer risks are below 1 x 10~6 at
       the locations of maximum concentration. The noncancer hazard indices for each of
       the population subgroups are significantly below 1.0 (do not exceed 2 x 10"2),
       indicating that adverse noncancer health  effects due to inhalation exposure to fugitive
       ash emissions are unlikely to result  from activities at the WTI facility.
             Area average cancer risks and HI values for the indirect exposure pathways
       are summarized in Table Vm-27.   Cancer risks and HQ values for individual
       substances are presented in  Appendix V-20.  Estimated cancer risks and HI values for
       the indirect exposure pathways are  significantly less than cancer risks and HI values
       estimated for the inhalation  pathway.  For adult residents, lifetime cancer risks due to
       average  indirect exposure to fugitive ash emissions from  the WTI facility are below
Volume V
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       8 x 10'12.  For children (1 to 6 years old) and school-age children (7 to  12 years old).
       lifetime cancer risks for indirect exposure to metals in fugitive ash emissions are not
       expected to exceed 4 x 1CT11 and 1 x ID"", respectively.  The highest cancer risks are
       estimated for the areas east and west of the site for all subgroups.  Noncancer H3
       values are estimated to be significantly below 1.0 in all quadrants; the highest average
       HI value estimated, 5 x IQr6, is predicted for  the eastern and western quadrants for
       children (1 to 6 years old).
              Cancer risks and HI values for the indirect pathways of exposure are also
       estimated for the location of maximum concentration, as shown in Table VTH-27.
       Cancer risks are below 2 x 10"10 at the location of maximum concentration for all
       subgroups. The noncancer hazard indices for each of the population subgroups are
       significantly below 1.0 (do not exceed 3 x 10~5), indicating that adverse  noncancer
       health effects due to indirect exposure to fugitive ash emissions are unlikely to result
       from activities at the WTI facility.

F.  Uncertainties
       As emphasized in the recent U.S. EPA exposure assessment guidelines (U.S. EPA
1992b), identification and quantification of uncertainties and variability is an important
element of the risk characterization.  Various sources of uncertainty have been  identified in
each of the preceding chapters, and an overall assessment of uncertainty in the  HHRA is
conducted in Chapter DC.  The following sections discuss uncertainties associated with the
risk characterization  process and the risk estimates.

       1.     Uncertainties Associated with the Risk Characterization Process
             Uncertainties associated with the methodology used to characterize risks are
       based on a number of assumptions used in the risk characterization process.  The  key
       assumptions, the basis for each, and the estimated effects (including magnitude and
       direction of effect) on risks are summarized in Table Vni-28.  For many of these
       methodological assumptions, potential effects  on the overall results of the HHRA are
       judged to be minor.  The primary exception is the estimation of impacts at the point
       of maximum concentration within each subarea, which assumes that an individual
       (resident, subsistence fanner, etc.) will be located at this point continuously for the
       entire exposure duration.  However, this assumption is necessary to provide an
       indication of the range of potential risks within a subarea.
                                                                i"1
             As noted in section A of this chapter, there is some uncertainty associated  with
       additive risks (i.e., summing cancer risk estimates and hazard quotients  across
       chemicals and exposure pathways).  The HI approach for the noncarcinogenic effects

Volume V                               \rrrr 01
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       of chemicals assumes that multiple sub-threshold exposure could result in an adverse
       effect and that a reasonable criterion for evaluating the potential for adverse effects is
       the sum of the hazard quotients for individual chemicals. This approach is presented
       in the U.S. EPA guidelines for assessing risks of chemical mixtures (U.S. EPA
       1986b), which conclude that the dose-additive approach is appropriate for evaluating
       noncancer effects of mixtures when the chemical constituents are present at low doses
       and also induce the same toxic effect in the same organ by the same mechanism of
       action.
              This approach has been supported by several recent studies conducted to
       examine the relationship between the development of toxicity and dose using mixtures
       of chemicals with exposures at or near the NOAEL and LOAEL values for individual
       components of the mixture.  Jonker et al. (1990) tested a group of eight arbitrarily
       selected chemicals in rats and found that when administered at dosages of 1/3 to 1/10
       of their respective NOAELs, no adverse effects were observed.   In this same study,
       when the chemicals were administered at the levels of individual NOAELs, mild
       toxicity was observed, which tended to be of minor toxicological significance. A
       range of responses was observed when chemicals were administered at the individual
       LOAEL values. Some effects were more severe than those observed when the
       compounds were administered singly at the same doses,  while others were less severe.
       Certain effects observed when compounds were given individually at the LOAEL
       level were not induced by the mixture while other effects not seen after treatment with
       the individual chemicals were caused by administration of the mixture.
             In a follow up study from this laboratory  (Groten et al. 1994), a group of nine
       arbitrarily selected chemicals were administered to rats for four weeks.  In this study,
       when the individual chemicals were given at 1/3  of their NOAEL levels, no adverse
       signs of toxicity were observed. When animals were administered doses equal to
       NOAEL levels, only minimal signs of toxicity  were reported. When the doses of the
       individual compounds were equal to their respective LOAELs, effects ranging from
       antagonism to additivity to synergism were observed depending on the endpoint
       studied.
             In subsequent studies, the authors tested a group of four nephrotoxic chemicals
       known to exert renal toxicity via different modes of action.  Following administration
       to rats (Jonker et al.  1993a) over a four week period (Jonker 1993b),  no adverse
       effects were observed at doses of individual compounds equal to ,1/4 of their NO A FT
       levels.  However, when the four chemicals were given at their respective LOAELs,
       the renal toxicity in male rats was  more severe than when the chemicals were
       administered individually.
Volume V
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              In a more recent study (Jonker et al. 1994), the authors administered four
       nephrotoxic chemicals (thought to exert toxicity by the same mechanism of action) to
       rats over a period of four weeks.  When these chemicals were administered at levels
       equal to the individual NOAEL values, a slight increase in kidney weight was
       observed relative to controls.  When the chemicals were given at doses equal to  1/2
       their respective LOAELs, clear nephrotoxicity was observed.  No data were presented
       for administration of these compounds at levels below the individual NOAEL values
       for the individual chemicals. These data are consistent with the hypothesis that
       adverse systemic effects would not be expected from exposure to a mixture in which
       the individual chemicals are present at levels substantially lower than.the threshold for
       toxicity associated with individual chemicals in the mixture.
              This conclusion  is further substantiated by studies conducted on complex
       mixtures of groundwater contaminants under the National Toxicology Program
       (NTP).  In these studies, a mixture of 25 groundwater contaminants commonly
       identified in the groundwater near hazardous waste sites was administered to rats and
       mice via drinking water for periods ranging from 14 to 90 days, and various
       endpoints for toxicity were examined  (Chapin et al. 1989; Yang et al.  1989; Simmons
       et al. 1994).  The results of these studies are consistent with the hypothesis that
       systemic toxicity subsequent to exposure to a complex mixture would not be expected
       when the concentration  of individual components of the mixture are well below their
       respective  toxicity threshold values (NOAELs).
              The limited  studies performed  to date are consistent with the assumption of
       additivity of noncancer  health effects of chemicals  in complex environmental
       mixtures, as long as the doses of the individual compounds are below their respective
       toxicity thresholds or NOAELs.   U.S. EPA risk assessments utilize reference doses
       and reference concentrations of the contaminants of concern as the basis for
       evaluating  noncancer health effects; these measures of toxicity are two to three orders
       of magnitude below the NOAELS and/or LOAELs observed for the compounds.  If
       the hazard quotient of a chemical is greater than one, then there is potential concern
       for noncancer health effects due to the presence of that chemical.  This approach is
       clearly  more health protective than comparing estimated exposures to the measured
       toxicity threshold for contaminants. Hence the additivity assumption is appropriate
       for the  HHRA.
              In contrast to the mechanisms of action for  noncancer health effects which are
                                                                f
       assumed to have thresholds, it is assumed tnat  there is no threshold for most
       genotoxic carcinogens.  There are a number of examples of interactive effects of two
       or more chemicals in inducing cancer.  For example, synergism was observed

Volume V                               TTTTT i«
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       between tobacco smoking and occupational exposure to asbestos in inducing cancers
       in workers.  Of the large number of studies of potential interactions among
       carcinogenic constituents of a mixture, most have used doses of the individual
       components known to increase tumor incidences above those seen in controls.  Only a
       few studies of chemical mixtures have examined the issue of low-level exposure to
       known carcinogens.  As an example, Ito et al. (1991)  gave five heterocyclic amines to
       rats in their diets for six weeks at levels of l/5th and l/25th of the dose known to
       cause liver tumor formation for each individual amine. A slight increase in
       glutathione S-transferase placenta! form (GST-P) positive foci was observed in  rats
       fed the mixtures as compared to rats fed the  individual compounds.  The researchers
       concluded that the  results were consistent with additivity or slight synergism.
              In work of Hasegawa et al. (1994), 10 carcinogenic, heterocyclic amines were
       administered to rats at 1/10 or 1/100 of the carcinogenic dose for individual
       compounds in the diet for six weeks.  When examined, it was found that rats
       receiving 1/10 of the carcinogenic dose demonstrated an increased incidence of GST-
       P positive foci consistent with additive effects or slight synergism.  In the 1/100 test
       group, there was no observable difference in the number of positive foci as compared
       to controls. Based on the results of the studies described above, it  is assumed for the
       purposes of the HHRA that exposure to individual carcinogens in most environmental
       mixtures are well below the doses of such chemicals known to cause cancer in
       experimental animals and/or occupationally exposed humans.
             As noted by U.S. EPA (1989b), there are several limitations to the assumption
       of additivity of carcinogenic chemicals. One of these limitations arises from the fact
       that risks are based on unit  cancer risks that are derived as upper 95th percentiles of
       the probability distributions of cancer potency. Because upper 95th percentiles  of
       probability distributions are not strictly additive, the total cancer risk estimate can
       become artificially  more conservative as risks from a number of carcinogens are
       added. Secondly, the approach routinely applied in cancer risk assessment treats all
       carcinogens equally, regardless of the weight-of-evidence class to which a carcinogen
       is assigned. Each class is given equal  weight; known carcinogens (class A) are
       considered equal to probable and possible carcinogens  (classes B and C) in the
       summation of risks.  Finally, the mechanism  of toxicity of any two chemicals may not
       be the same and, in fact, might not be independent.  Cumulative cancer risk estimates
       assume similar mechanisms of action and  that mixtures of chemicals do not act
       antagonistically or synergistically.  Although deviation  from an additive response has
       been  demonstrated  at high exposure levels in both laboratory animal models and
       epidemiological studies,  it has been suggested that risks may be additive at low  doses.
Volume V
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        This concept is supported by behavior of both the multistage and two-stage clonal
        expansion models of carcinogenesis, the additive-background model, and the
        multiplicative relative risk model (Krewski and Thomas 1991).  The National
        Research Council has concluded that in the absence of specific information on
        chemical interactions at relevant doses, the principle of low dose additivity of risks
        continues to offer the best approach to cancer risk assessment for mixtures (NRC
        1988).

        2.     Uncertainties Associated with the Risk Estimates
              As noted above, Chapter DC presents  a quantitative analysis of .the uncertainties
        involved in each step of the process of estimating indirect risks of two
        substances—2,3,4,7,8-PeCDF and arsenic—for a subsistence farmer in  subarea El
        (the subarea of greatest impact). This analysis is intended to evaluate the sources of
        uncertainty affecting the indirect risk estimates.  Although subsistence farmers may
        not comprise a significant fraction of the population, the conclusions drawn from the
        analysis concerning sources of uncertainty likely apply to  risk estimates for other
        subgroups as  well.

       3.     Uncertainty Associated  with the Uncharacterized Emissions
              A source of uncertainty in estimating risk not specifically addressed in Chapter
       IX is the uncertainty associated with uncharacterized emissions.  Although significant
       measurements have been obtained to characterize emissions from the facility, it is
       known that the characterized fraction of the organic emissions from the incinerator
       stack accounts for approximately 40 percent of the total organic emissions (as
       discussed in Chapter V of Volume HI). The  emission rates of the constituents within
       the characterized fraction are likely to be relatively accurate; however, the compounds
       emitted in the uncharacterized fraction are unknown. To provide an indication of the
       potential effects on total estimated risks, it is possible for the purpose of illustration to
       prorate the average cancer risks  to the subsistence farmer in  subarea El associated
       with the non-dioxin organic compounds by a factor of 2.5  to account for the
       uncharacterized fraction.  The inherent assumption  in the prorating process is that the
       cancer potency of the uncharacterized fraction is equal to the cancer potency of the
       characterized fraction.  Total cancer risks to the subsistence farmer in subarea El are
       estimated to be 1.3xlO~6 in this assessment (as discussed earlier), with  non-dioxin
       organic compounds accounting for approximately 24 percent  of the risks.  When the
       prorating  factor of 2.5 is applied to the risks from non-dioxin organic compounds,  the
       average cancer risks to a subsistence farmer in subarea El  become 1.8 x 10"6.  Non-
Volume V
                                       VTTT-'?7
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       dioxin organic compounds would account for 44 percent of these risks, and there
       would be a 36 percent increase in total risk.
              An additional source of uncertainty exists when emissions of unknown
       composition occur associated with abnonnal operations of the incinerator that in some
       instances results in emission limit exceedances or automatic waste feed cutoffs.  An
       analysis of total hydrocarbon (THC) measurements from April 1,  1995 to March 31.
       1996 indicates that THC excursions above the 1 ppm level used in the risk assessment
       occurred intermittently throughout the year.  The annual average THC value
       incorporating the periodic fluctuations in THC levels was estimated to be up to 30
       percent higher than what was observed during stack tests.  Although ihe emission
       composition during abnonnal operations is unknown, if it is assumed that the cancer
       potency of constituents in emissions during abnonnal operations is equal to the cancer
       potency of constituents in normal emissions, the overall cancer risk would increase by
       no more than 30 percent.  Given that the average cancer risk to a subsistence farmer
       and child (the subgroups with the maximum predicted exposures) is 1.3 x  10~6, a 30
       percent increase in estimated cancer risk due to an increase in THC emissions would
       not result in significant cancer  risks to the population.

       4.     Uncertainties Associated with the Selection of Surrogate Chemicals
              An initial step in  conducting the human health risk assessment  (HHRA) was to
       identify the chemicals that may be released from the WTI stack and select a subset of
       these chemicals for quantitative evaluation in assessing potential risks through indirect
       routes of exposure.  A surrogate chemical selection process was developed,  as
       described in Chapter IV  of the  HHRA, which consisted of a scoring system  used to
       rank the chemicals.  The ranking system was developed  based on an understanding of
       the key parameters that influence estimates of chemical risk via indirect pathways of
       exposure.  Chemicals likely to  account for most  of the anticipated risk from  the
       facility were selected based  on  this  ranking process.  As a conservative measure,
       additional chemicals that were not initially retained based on the ranking system were
       also included based on professional judgment to ensure that potentially important
       chemicals were  not inadvertently excluded in the ranking process.
              The risks estimated in the risk assessment were used to investigate whether the
       chemicals added to the surrogate chemical list based on professional judgment or
       chemicals that ranked low on the list of selected surrogates contributed significantly to
       the risk estimates.  Figure Vin-3 contains a listing of the 29 carcinogens that were
       selected for quantitative evaluation in the HHRA.  The chemicals are ranked
       according to the score received from the surrogate chemical selection process. Also
Volume V
-------
       shown in Figure VIII-3 is the cumulative percentage of total risk contributed by these
       29 chemicals, as estimated from the results of the HHRA for the adult subsistence
       farmer.
              As evident from Figure VIII-3, if the risk assessment were conducted for only
       the top 10 chemicals by rank, cancer risks would be within a factor of 2 of the
       estimated risks for all 29 chemicals.  If the list of chemicals was reduced by half, risks
       would be within approximately  15 percent of the estimated risks for 29 chemicals.
       Thus, the incremental addition of the last 10 to 15 chemicals does not make a
       significant contribution to the estimated total risks.  Based on this analysis, it can be
       inferred that although additional chemicals could be subjected to quantitative risk
       evaluation, it is unlikely that chemicals with lower ranks than the selected surrogate
       chemicals would materially change the cancer risk assessment results.  As indicated in
       Chapter IV, it should be recognized that the chemical- and site-specific parameters used
       in the surrogate chemical selection process are used with many other chemical-  and
       site-specific parameters in complex equations in the risk assessment.  Thus,  the relative
       scores estimated using the scoring algorithm do not necessarily reflect the relative risks
       estimated in the risk assessment.
              A similar analysis was conducted for the chemicals with noncancer effects,
       although the estimated hazard index (HI) for the subsistence farmer in the subarea with
       the maximum impact was several orders  of magnitude below a level of concern.  Of the
       8 chemicals selected for quantitative evaluation for noncancer effects, the top 5  ranked
       chemicals accounted for 99.7 percent of the estimated HI value for the  site.  It is highly
       unlikely that a chemical was excluded that would result  in a total HI approaching levels
       of concern.

       5.    Uncertainties Associated with Characterizing Breast Milk Ingestion Risks
             A review of the scientific literature indicates that heavy metals have been
       detected in the breast milk of lactating women, likely due to exposure from
       environmental sources. For example, studies have indicated breast milk concentrations
       of lead from exposure to tap water, and emissions from  smelters and the metallurgical
       industry (Kacew  1994, Moore et al.  1982, Namihira et al. 1993); cadmium from
       smoking (Radisch et al. 1987, Eynon 1985),  and mercury from seafood (Wormworth
       1995, Grandjean 1994).  At present, however, U.S. EPA (1990a, 1993a, 1994a)
       guidelines do not provide a methodology for estimating  the transport of metals into
       breast milk.  This potential route of exposure, therefore, was not evaluated in the
       HHRA.
Volume V                               VIII-29
-------
       To evaluate the potential uncertainty associated with not evaluating exposure to
 metals in breast milk, an analysis was conducted to compare relative concentrations of
 contaminants in cows'  milk to provide an indication of the potential partitioning of
 metals into human breast milk.  Based on a one gram per second emission rate, the
 cow milk concentration of the chemicals of potential concern was estimated for the
 subarea of maximum impact (Subarea El).  The relative concentrations of 2.3.7.8-
 TCDD, benzojajpyrene, arsenic, beryllium, and mercury were compared.  Table
 Vin-29 summarizes the relative concentrations of three metals—arsenic, beryllium.
 and mercury—as compared to 2,3,7,8-TCDD and benzofajpyrene, assuming a unit
 emission rate from  the facility.  As indicated in Table Vm-29, the partitioning of
 these metals is more than 1,000 times lower that the partitioning of the organic
 compounds into cows'  milk.
       It should be noted, that organic forms of mercury  (e.g., methylmercury) are
 more likely to partition into fat (e.g.  milkfat) than inorganic metals; however,
 exposure to organic forms of mercury was  not estimated to  be significant in this
 assessment.  Organic forms of mercury are most likely associated with surface water.
 drinking water derived from surface water bodies, and fish caught locally.  As
 indicated in this assessment, the potential pathways of exposure associated with these
 sources are not estimated to be significant.
       In summary, although transport of metals (inorganic  and organic forms) into
 breast milk is possible, the partitioning is expected to be significantly less than  the
 organic compounds evaluated in this assessment and the sources of exposure are not
 estimated to be significant.  Therefore, it is unlikely that exposure to metals would
 constitute a significant source of risk  for breast-feeding infants.

 6.     Uncertainties Associated with Methylmercury Risks
       The potential for adverse noncancer  health  effects associated with exposure to
 methylmercury in fish is estimated  in this risk assessment  for a hypothetical subgroup
 of the population that derives a significant fraction of their diet from locally caught
 fish (subsistence fishing).  Potential risks  are estimated based on subsistence
 consumption of fish caught in the Ohio River, Little Beaver Creek,  and Tomlinson
 Run Lake, as described in Section  C.5.a. of this chapter.
       The primary contributor to total noncancer HI values in each of these water
 bodies is exposure to methylmercury, which is estimated to bioaccumulate
 significantly in fish.  The bioaccumulation potential for a specific substance in fish is
 represented by its bioaccumulation  factor  (BAF).  This factor is used in the fate and
transport modeling (Appendix V-7) to estimate the concentration of  substances in fish
-------
       tissue.  Significant uncertainty exists, however, concerning the BAF for
       methylmercury. The value of BAF for methylmercury used in this assessment is
       85,700 L/kg from U.S. EPA's (1985) Ambient Water Quality Criteria for Mercury.
       However, U.S. EPA (1995f) developed for the Mercury Study to Congress a
       recommended value  of 350,000 L/kg, which is a factor of four greater than the value
       used in this risk assessment. The maximum  estimated HQ value for exposure to
       methylmercury in fish by a subsistence fisherman is 0.0028 (2.8 x 10'3) at Tomlinson
       Run Lake.  The total noncancer HI value for subsistence fishing at this  location is
       0.004 (4 x 10'3).  An increase  in the methylmercury BAF value used in this
       assessment would result in a corresponding increase in the estimated HQ value for
       methylmercury. Thus, use of  a BAF value for methylmercury of 350,000 L/kg
       would not likely result in significantly elevated risks for this pathway.

G.     Comparison of Incremental Dioxin and Furan Exposure to Expected Background
       Exposure
       As mentioned in Chapter m, the lack of RfD and RfC toxicity values for the dioxin-
like compounds means that potential adverse noncancer effects from exposure to dioxins  and
furans cannot be directly quantified.  Therefore, noncancer HQ values cannot be calculated
for the potential risk from exposure to dioxins and furans. As an alternative, it is useful to
compare the estimated incremental exposures to the predicted or expected background
exposure levels.  This will serve as an indicator of the potential impact on human health  by
showing the additional contribution of the incremental exposure from incinerator emissions to
the overall  body burden of dioxin-like compounds from background exposures.
       To make the comparison, it is  necessary  to calculate the toxic equivalent (TEQ) dose
for the estimated exposure to the dioxin-like compounds. This calculation is performed using
the LADD  data for the adult subsistence farmer in Subarea El (Table VII-18).  For each
toxic dioxin and furan congener, the combined exposures from soil, water, and food are
multiplied by the corresponding TEF value  (Table IH-2) to obtain a TEQ dose for each
congener.   The TEQ doses for each congener are summed to  yield a total TEQ dose for the
dioxin and  furan congeners.   The TEQ dose calculated in this manner is  found to be 7 x  10"12
mg TEQ/kg-day.
       The U.S. EPA discusses estimates of background exposure to dioxins and furans in its
"Draft Dioxin Reassessment" (U.S. EPA 1994b).  The range  of background exposures to the
U.S. adult population has been estimated as 1 x  10~9 to 3 x 10'9 mg TEQ/kg-day.  This
includes the predicted background exposure from multiple sources including the food chain
pathway, the inhalation pathway, and  soil ingestion.
Volume V
-------
        Therefore, the LADD of 7 x 10"12 mg TEQ'kg-day for a subsistence farmer living in
  the subarea of greatest impact is predicted to be less than 1 percent of the average daily
  background dose expected for the U.S. adult population.  Consequently, the probability is
  low that the incremental exposure due to emissions from WTI would result in a significantly
  increased body burden of dioxin-like compounds for the majority of the population in the
  vicinity of the incinerator.
Volume V
-------
TABLE Vm-1
Target Organ(s) for Substances of Potential Concern with
Potential Adverse Noncancer Effects
Compound
Target Organ(s)
PICs and Residual Organic Compounds
Bis(2-ethylhexyl)phthalate
Carbon tetrachloride
Di(n)octyl phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
liver
liver, kidney, CNS
CNS, liver
CNS, liver
liver, skin
kidney
respiratory tract, gastrointestinal tract
CNS
Metals
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Mercury
Nickel
Selenium
Silver
Thallium
Zinc
respiratory tract, heart, blood
CNS, skin
respiratory tract, cardiovascular system
respiratory tract*
kidney, respiratory tract
respiratory tract, kidney, skin'
CNS, peripheral nervous system, kidney, gastrointestinal
tract
respiratory tract, decreased body and organ weights
respiratory tract, gastrointestinal tract, CNS
skin, respiratory tract
liver
respiratory tract, blood
Notes:
CNS = central nervous system
a - Reference Dose (RfD)/Reference Concentration (RfC) based on No Observable Adverse Effects Level (NOAEL)
Target organ indicated in bold is endpoint used to develop RfD/RfC
Sources.
Integrated Rjsk Information System (TRJS) **
Agency for Toxic Substances and Disease Registry (ATSDR) Public Health Service. 1987-1995. Ttuacological profiles
Clayton, G.D. and F.E. Clayton, eds (1994). Pony's industrial hygiene and toxicology. 4th edition. John Wiley & Sons,
Inc., New York.
Volume V
-------
TABLE Vm-2
Components of Risk Descriptors and High-end Subgroups Evaluated in the Sensitivin Analysis
Risk Descriptor
Area Average
Maximum
Emission
Rate
Average
Average
Exposure
Factors
Average
Average
Atmospheric
Dispersion/Deposition
Modeling
Subarea average
concentration and
deposition
Point of maximum
concentration in subarea
Sensitivity Analysis of Exposure Parameters
Exposure Subgroup
Adult subsistence fanner1
Child of a
subsistence farmer1
Exposure Parameter Values
• Average exposure values except:
- High-end exposure duration
- High-end food ingestion rates
• Average emission rates
• Average exposure values except:
- Food ingestion rates.
• High-end emission rates
Atmospheric
Dispersion/Deposition
Modeling
Subarea average
concentration and
deposition
Subarea average
concentration and
deposition
Note:
1 - In the sensitivity analysis of exposure variability, the two exposure parameters with the greatest effect on nsk when set
at the high-end value were applied in estimating dose and risk, is indicated in the table. For example, for the
subsistence fanner, use of high-end food ingestion rates and high-end exposure duration resulted in the largest increase
in total risk.
Volume V
-------
TABLE Vm-3
Estimated Total Inhalation Cancer Risks for Substances of Potential Concern
Subarea
Concentration
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Ml
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Population Subgroup
Resident
Adult
3 x 10*
1 x 10'7
2x 10*
3x10*
7x 10*
1 x 10*
2x 10*
6x 10*
7x 10*
2x 10*
3x Iff*
5x 10-9
2x 10*
6x 10*
1 x 10*
2x 10*
5x 10*
7x 10-*
2x 10*
4x 10*
6x 10*
2x 10*
3x 10*
4x 10"'
Resident
Child
8x 10*
2x ID"7
4x 10*
8x 10*
2x 10*
3x10*
4x 10*
1 x 10-7
2x10*
4x 10*
8x lO*
1 x 10*
5x 10*
2x 10"7
3 x 10*
6x 10*
1 x 10*
2x 10*
4x 10*
1 x 10"7
2x 10*
4x 10*
7x 10*
1 x 10*
School-Age
Child
5x 10*
2x Iff7
2x 10*
5x 10*
1 x 10*
2x10*
2x10*
8x 10*
1 x 1O*
2x 10*
5x Iff*
7x Iff*
3x 10*
1 x Iff7
2x 10*
3 x 10*
7 x 10*
1 x 10*
2x 10*
6x 10*
9x Iff*
2x 10*
4x Iff*
6x Iff9
Farmer
Adult*
7x Iff8
2 x 107
3x 10*
8x 10*
1 xlO*
2x 10*
3x 10*
1 xlff7
2x10*
3x 10*
7 xlff*
1 x 10*
5x 10*
1 x ID'7
2x 10*
5 x 10*
1 x 10*
2x 10*
3 x 10*
9x 10*
1 x 10*
3x 10*
6x Iff9
9x Iff9
Farmer
Child"
8 x 10-*
2 x 10'"
4 x 10-*
8 x 10-8
2x 10-6
3 x Iff8
4 x 10*
1 x 10'7
2x 10*
4x Iff8
8 x lO'9
1 x Iff8
5 x 10*
2 x lO'7
3 x 10*
6x 10*
1 x 10*
2x 10*
4x 10*
1 x Iff7
2x 10*
4x 10*
7 x Iff9
1 x 10*
Notes:
a - Inhalation cancer risks are the same for farmers and subsistence farmers (child and adult). , •
Volume V
-------
TABLE VflW
Estimated Total Inhalation Noncancer Hazard Indices for Substances of Potential Concern
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Population Subgroup
Resident
Adult
1 x 10'2
4 x 10'2
6 x lO'3
1 x ID"2
3 x Iff3
4x 10-3
6x icr3
2x ID"2
3x lO"3
6x 10"3
1 x 10"3
2x 1(T3
8x 10-3
2x 10-2
4x 10"3
9x 10-3
2x la3
3 x 10-3
6x ID"3
2x 10-2
2x Iff3
6x icr3
1 x 10-3
2x 10"3
Resident
Child
5x icr2
1 x 10-'
2x 10"2
5x 10-2
9x 10-3
1 x 10-1
2x ID"2
8x Iff1
1 x 10-2
2x 1(T2
5x Iff3
7x 10"3
3 x ID"2
9x 10-2
2x 10-2
3 x 10"2
7 x 10°
1 x ia2
2 x ia2
6x ID"2
9x lO0
2x Iff2
4x 10-3
6 x Iff3
School- Age
Child
3x 1(T2
9x 10-2
1 x 1(T2
3x 10-2
6x ID"3
9x Iff3
1 x Iff2
5x 1(T2
6x Iff3
1 x 1(T2
3 x lO4
4x 10"3
2x 10-2
6x Iff2
9x Iff3
2x icr2
4x Iff3
7 x lO'3
1 x 10'2
4x 1(T2
5x 10-3
1 x 1(T2
2x ID"3
4x 10-3
Fanner
Adulf
1 x 10":
4 x 10-
6 x lO'3
1 x 10'2
3 x 103
4 x 10°
6x 10"3
2 x 102
3 x 1(T3
6x Iff3
1 \ Iff3
2x 10-3
8x Iff3
2 x 102
4 x 1C'3
9x 1(T3
2x 1(T3
3 x Iff3
6 x 1(T3
2 x 10-2
2x 10-3
6x 10"3
1 x ia3
2x 1(T3
Farmer
Child'
5 x 10:
1 x 10
2 x 10':
5 x 10:
9 x 10"
1 x 10':
2 x 10:
8 x 10:
1 x 10':
2 x 10 :
5 x 10-'
7 x ID''
3 x 10':
9 x 10:
2 x 10 :
3 x 10':
7 x 10°
1 x 10":
2 x lO'2
6 x 10":
9 x ID'3
2 x 10-:
4 x 10°
6 x ID'3
Note:
a - Inhalation noncancer HI value* are the ume for farmers and nibiistence farmers (child and adolt).
Volume V
-------
TABLE VIII-5
Comparison of Predicted Acid Gas and Particulate Matter Concentrations with NAAQS
Subarea
El
E2
E3
Nl
N2
N3
SI
S2
S3
Wl
W2
: W3
Estimated Average and Maximum Air Concentration 0*g/mJ)
(NAAQS in parenthesis)
NO,
(100 ng/m3)
Average
7x la1
3 x 10-'
2 x 10 '
3 x 10'
1 x 10'
6 x Ifr2
3 x 10 '
2 x 10 '
7 x 102
5 x 10 '
2 x 10'
1 x 10 '
Maximum
2
8 x 10 '
2x ia1
9 x 10 '
3 x 10'
9x ia2
1
3x icr1
1 x 10-'
1
5 x ia1
2x ia'
so,
(80 wg/m')
Average
3x ia2
i x ia2
6x 10°
i x ia2
5x ia3
2 x 10 '
i x ia2
6x ia3
3 x ia3
2 x 102
9 x 103
4 x 103
Maximum
8x ia7
3x ia2
8x ia3
4x Ifr1
i x ia2
4x ia3
5x ia2
i x ia2
4 x 103
5 x 102
2 x 102
6 x 103
PM,,
(50 Mg/m3)
Average
2x 10"2
i x ia2
4x ia3
i x ia2
4x ia3
2x ia3
i x ia2
5 x 103
2x ia3
1 x 102
7 x 103
3 x 103
Maximum
7 x 102
2 x 102
7 x 103
3 x 10*
1 X 102
3 x 103
4 x 102
1 x 102
3 x ID"'
4x I02
. 2 x I02
5 x 10-'
Notes: ' ;
NAAQS: National Ambient Air Quality Standards. The average reported is the annual arithmetic mean.
NO,: NAAQS reported for nitrogen dioxide only. Predicted concentrations are for all nitrogen oxides.
SO,: NAAQS reported for sulfur dioxide only. Predicted concentrations are for all sulfur oxides.
PM,0: NAAQS reported for paniculate matter less than or equal to 10 /im in diameter PM,0.
VII1-37
-------
TABLE Vrn-6
Estimated Cancer Risks Due to Exposure from Indirect Pathways
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Ml
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Population Subgroup
Resident
Adult
1 x 107
4x 107
6x 1O*
1 x 10"7
3 x 10*
4x 1O*
6x 1O*
2x 10-7
3 x 10*
6x 1O*
1 x 10*
2x 10*
9x 10*
3 x 107
4x 10*
9x 10*
2x 10*
3 x 10*
6x 10*
2x 107
2x 1O*
6x 10*
1 x 10*
2x 1O*
Resident
Child
3 x 1O7
1 x 10*
2x 1O7
3 x 1O7
7x 10*
1 x 1O7
2x 1O7
6x 1O7
7x 10*
2x 107
3 x 1O*
5x 10*
2x 107
6 x 1O7
1 x 107
2x 107
5x 10*
7x 10*
2x 1O7
4 x ID'7
6 x 10*
2 x 1O7
3 x 1O*
4x 1O*
Farmer
Adult
5x 1O7
2x 1O*
3 x 1O7
6x 1O7
1 x 10-7
2x 1O7
3 x 107
1 x 1O*
1 x 10-7
3 x 1O7
5x 10*
8 x 10*
4x 1O7
1 x 10*
2x 107
4 x 1O7
8x 10*
1 x 1O7
3 x 1O7
7 x 1O7
1 x 1O7
3 x 107
4x 10*
7x 10*
.Farmer
Child
5x 1O7
2x 10*
2x 1O7
5x 1O7
1 x 1O7
2x 1O7
2x 1O7
9x 1O7
1 x 107
2x 1O7
5x 1O*
7x 10*
3 x 1O7
1 x 10^
2 x 1O7
3 x 1O7
7x 10*
1 x 1O7
2 x 1O7
7 x 1O7
9x 10*
2x 1O7
4x 10*
7x 10*
School-
Age
Child
2x 1O7
7 x 10-7
1 x 1O7
2 x lO'7
4x 10*
7x 10*
1 x 1O7
4x 1O7
SxlO4
1 x 1O7
2x 10*
3 x 10*
1 x 1O7
4x 1O7
7x 10*
1 x 1O7
3 x 10*
5 x 1O8
1 x 1O7
3x 107
4x 1O*
1 x 1O7
2x 10*
3x 10*
Subsistence
Fanner
Adult
1 x 1O*
4x 1O6
6 x 1C'7
1 x 10*
3 x 1O7
4 x lO'7
6x 1O7
2x 10*
3 x ID'7
6x 107
1 x 107
2 x 10-7
9x 1O7
3 x 10*
4 x 1O7
9x 1O7
2x 1O7
3 x 107
6x 1O7
2x 10*
2x 107
6,x 107
1 x 1O7
2x 1O7
Subsistence
Farmer
Child
1 x 10*
4 x 10*
6 x 10-"
1 x 10*
2 x 107
4 x 10"
6 x lO'7
2 x 10*
3 x ID'7
6 x 10'7
1 x ID'7
2 x 107
8 x lO'7
2 x 10* I
4 x 10'7
9 x ID'7
2 x 1O7
3 x 1O7
6 x lO'7
2 x 10*
2 x lO'7
6 x 10-7 I)
1 x 1O7
2 x lO'7 1
Volume V
-------
TABLE VHI-7
Estimated Hazard Indices Due to Exposure from Indirect Pathways
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Population Subgroup
Resident
Adult
9x 104
2x ID"3
4x 1O4
7x MT1
2x 104
2x 104
4x 104
2x10-'
1 x 104
3x IV4
6x 10-5
1 x 104
6x KT4
1 x 103
2x 104
5x 104
1 x 1O4
1 x 1O4
5x10*
1 x ID"3
2x 104
4x 104
8x ID"5
Ix 104
Resident
Child
5x10°
1 x lO"2
2x ID"3
4x ID"3
9x 104
1 x 10"3
2x 10°
9x 1(T3
SxlO4
2x 10-3
3 x 104
5x 104
3x 10-3
7 x 10"3
1 x 10-3
2x 10°
6x 104
7x 104
3x ia3
8x 1(T3
9x 104
2x 10"3
4x 104
7x 10"
Farmer
Adult
2x 10"3
4x 10*
6x 1O4
Ix lO"3
3x 104
4X104
7X104
3x 10"3
2x 104
5x 104
1 x 104
2x 104
1 x 10*
2x 10°
4x 104
8x 1O4
2x 104
2x 104
SxlO4
3 x 10"3
3 x 104
7x 104
1 x 104
2x 1O4
Farmer
Child
8x 10-3
2x ia2
3x lO"3
5x ID"3
1 x 10*
2x ID"3
3xlO-3
1 x 10*
1 x ia3
2x 10-3
5x 104
7x 104
4x 10°
1 x 10-2
2x Ifr3
3 x 10"3
8x 104
9x 1O4
4x 10"3
1 x 10*
1 x 10"3
3 x 10"3
6x 104
9x 104
School-
Age
Child
3xlO-3
7xlO-3
Ix 10-3
2x 10"3
SxlO4
7x 104
IxlO"3
5x 10"3
4x10^
Ix 10°
2X10"
SxlO4
2x lO"3
4x 10-3
7x 104
1 x lO"3
3x 1O4
4x 10-1
2xlO-3
4x 10-3
5x 104
1 x ICC3
2x 104
4x 10"
Subsistence
Fanner
Adult
4x 10*
1 x 10-:
2x W
3x lO"3
7x 104
1 x 10-3
2x ID"3
7 x lO'3
6x 1O4
1 x 10"3
3x 10"
4x 10^
3 x lO"3
6x la3
1 x 10-3
2x 10-3
5x 104
6x 104
2x 10-3
7x ia3
8x 104
2x 10"3
4x 104
6x 104
Subsistence
Farmer
Child
2 x 10:
5 x 10 :
7 x 10 ••
I x 10":
3 x 10-3
4x 10-'
8 x ia3
3 x 10-:
3x ia3
6x 10-'
1 x 10'3
2x 10°
1 x 10-=
3x ia2
5x 10-'
9x 1O3
2x 10-3
3 x 1O3
1 x 10"2
3 x lO"2
3 x 10-3
8x ia3
2x 10-3
2x 10-3
Volume V
-------
TABLE VIII-8
Average Cancer Risks For an Adult Subsistence Fanner
Exposure
Pathway
Soil
Ingestion
Soil Dermal
Contact
Meat &
Egg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
[ngestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal »;
Contact
Total Risk
Subarea
El
7 x 10 '°
4 x 10 10
7 x 107
6 x 107
5 x 10*
4 x 10"
2 x 10"
NA
NA
1 x 10^
E2
2 x 10 10
1 x 10 10
3 x Ifr1
3 x 107
2 x 10*
1 x 10"
5 x la15
NA
NA
6 x 107
E3
1 x 10 10
6 x 10"
1 x 107
1 x 10'
1 x 10*
4 x 1016
2 x 1012
NA
NA
3 x 107
NI
4 x 10 10
2 x 10'°
3 x W
3 x 107
2 x 10*
NA
NA
NA
NA
6 x ia7
N2
1 x 10'°
7 x 10"
1 x 107
1 x 107
1 x 10*
6 x 10"
7 x 10"
NA
NA
2 x 107
N3
5 x 10"
3 x 10"
6 x 10*
5 x 10*
4 x ia'
NA
NA
NA
NA
1 x 107
SI
3 x 10 10
2 x 10 10
3 x ia7
3 x 107
2 x 10*
5 x 10"
2 x 10"
NA
NA
6 x ia7
S2
9 x ia"
5 x 10"
2 x 107
1 x 107
1 x 10*
NA
NA
NA
NA
3 x 107
S3
4 x 10"
2 x 10"
7 x 10*
5 x 10"
5 x 10"
NA
NA
8 x 10 "
4 x 10'2
1 x 1017
Wl
4 x 10 10
2 x 10 '"
5 x 107
4 x 107
4 x 10*
NA
NA
NA
NA
9x 107
W2
1 x 10'°
8 x 10"
2 x ia7
2 x 107
2x 10*
6x 10"
2 x 10"
NA
NA
4 x I07
W3
7 x 10"
4 x 10"
1 x ia7
8 x 10*
8 x 10'
6 x 10"
2 x 10"
NA
NA
2 x I07
Volume V
VIII 40
-------
TABLE VIII-9
Average Noncancer Hazard Indices for an Adult Subsistence Farmer
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat&
Egg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
HI
Subarea
El
i x \o>
2x 10*
2x ia'
2 x 10'
7 x 104
3 x 10-'°
2x 10*
NA
NA
4x IO3
E2
4x 10*
9x Ifr7
7x \0*
6x IO4
4*10*
1 x ia'°
5x ia'
NA
NA
2 x 10 3
E3
2x 10*
4x ia7
2x 10*
3 x 10^
2x 10*
4x Ifr"
2 x 10'
NA
NA
7 x 10*
Nl
6x 10*
1 x 10*
1 x 10°
8x 104
4x \0*
NA
NA
NA
NA
2 x 10'
N2
2x 10*
4 x IO7
3 x 10*
3 x 10*
1 x 10*
1 x \09
3 x 1O*
NA
NA
8x 10*
N3
9 x 107
2x ia7
2x 10*
1 x \0*
6x 10*
NA
NA
NA
NA
4 x 10^
SI
5x 10"6
1 x 10*
8 x 10-*
6x 10^
4x HT1
4 x la10
2x IO*
NA
NA
2x W
S2
2x 10*
4x ia7
3x 10^
2x ID4
2x 10*
NA
NA
NA
NA
6x \0*
S3
7 x IO7
2 x IO7
1 x 10*
1 x \0*
7 x IO5
NA
NA
2 x 10'
4 x 10«
3 x \0*
Wl
6x 10-*
1 x 10*
1 x 10'
9x 10^
5x 10^
NA
NA
NA
NA
3 x IO1
W2
3 x 10*
6x ia7
4x 10*
3x 10^
2x 10^
5 x 10 10
2x 10*
NA
NA
1 x IO1
W3
1 x 10*
3 x IO7
2x 10^
2x 10*
1 x 10*
5 x 10'°
2 x 10"
NA
NA
5 x 10"
Volume V
                                                                  VIII-41
-------
TABLE V1IMO
Chemical-specific Carcinogenic Risks for the
Adult Subsistence Fanner in Subarea El (Area Average)
Chemical
2,3,7,8-TCDD
1,2,3,7,8-PeCDD
1,2,3,4,7,8-HxCDD
1,2,3,6,7,8-HxCDD
1,2,3,7,8,9-HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3,7,8 PeCDF
2,3,4,7,8-PeCDF
1,2.3,4,7,8-HxCDF
1,2,3,6,7,8-HxCDF
1,2,3,7,8,9-HxCDF
2,3,4,6,7,8-HxCDF
1,2,3,4,6,7,8-HpCdF
1,2,3,4,7,8,9-HpCDF
OCDF
Soil Ingestion
and Dermal
Contact Risk
i x 10"
4 x 10"
8 x 10'1
1 x 10"
9 x 10"
I x 10"
5 x 10"
1 x 10"
2x 10"
3 x 10'°
1 x 10'°
1 x 10'°
3 x 10"
1 x 10'°
8x 10"
1 x 10"
2x 10"
Total Meat and
Egg Ingestion*
Risk
7x 10'
6x 10'
8x 10'
2x 10'
3 x 10'
2 x 10'
4x 10'
2 x 10'
5x 10'
3x 10'
3 x 1O'
6x10'
1 x 10'
4x 10'
3 x 1O'
7 x 10'°
3 x 1O'
Total Dairy
Product Ingestionb
Risk
5x 10'
4x 10*
6x 1O'
1 x 10'
2x 10'
2x 10'
3 x 10'
2x 10'
4x 10'
2 x 107
2x 10'
4 x 10'
1 x 1O'
3x 10'
2x 10'
5 x 10'°
2x 10'
Total Fruit and
Vegetable
Ingestion*
Risk
2 x 10'°
2x 10'
4 x 10'°
1 x 10'°
1 x 10'°
7 x 10'°
9 x 10'
3 x 10'°
8 x 10W
1 x 10'
1 x 10'
3 x 10'
8 x 1010
2x10'
8 x 10'°
6x 10"
2x 10'
Riter Water
Ingestion and
Dermal Contact Risk
2 x 10"
4 x 10"
1 x 10"
2 x 1O"
3 x 10"
1 x 10"
4 x 10"
2 x 10"
3 x 10"
4 x 10"
2 x 10"
2 x 10"
4 x 10"
2 x 10"
9x 10"
I x 10":
9 x 10"
Infant Breast Milk
Ingestion Risk
7x 10'
6 x 10'
8x 10'
2 x 10'
3 x 10'
3x 10'
4x10'
2x 10'
5x10'
3x 10'
3x 10'
6x 10"
1 x 10'
4x 10'
4x 10'
7x 10'"
4 x 10'
TOTAL
CANCER
RISK'
1 x 10'
1 x 10'
1 x 10'
4x 10'
SxlO'
5x 10'
8x 10'
4x 10'
9x 10'
5x 10'
6x 10'
1 x 10'
2x 10'
7x 10'
6x 10'
1 x 10'
8x 10'
Volume V
                                                                  VIII-42
-------
TABLE VUI-10 (continued)
Chemical-specific Carcinogenic Risks for the
Adult Subsistence Farmer in Subarea El (Area Arerage)
Chemical
Tetrachlorobiphenyl
HexachloFobiphenyl
HepUchlorobiphenyl
Benzo(i)pyrene
Bcnzo(b)fluoranthene
BU(2-ethylhexyl)phthaIate
Carbon tetrachloride
Dibenz(a,h)anthracene
Heplachlor
Hexachlorobenzene
Hexachlorobutadiene
Indeno(l ,2,3-cd)pyrene
Arsenic
Beryllium
Soil Ingestion
and Dermal
Contact Risk
8 * ia"
1 X Iff"
1 X Iff"
2 x ia"
i x ia"
2 x iff14
1 X Iff11
6 x ia"
3 x Iff14
2x Iff"
3 x Iff11
6 x Iff"
6 x Iff"
4 x Iff"
Total Meat and
Egg Ingestion'
Risk
1 x Iff10
6 x Iff"
1 x Iff'
1 x Iff1
6x Iff9
2x Iff1
1 x 10"
2x Iff1
4 x 10"
2 x 10'°
2 x 10"
1 x Iff'
3 x Iff"
5 x Iff"
Total Dairy
Product digestion*
Risk
6x 10"
4 x 1O"
1 xlff'
1 xlff7
6x Iff'
2x Iff*
9 x 10"
2 xlff1
4 x 10"
1 x 10™
1 x 10"
2x10'
3 x 10"
1 x Iff"
Total Fruit and
Vegetable
Ingestion'
Risk
2 x Iff"
2 x 10"
1 x 1O"
7x10"
4 x 10"
8 xlff9
2 x Iff"
7 x Iff"
2 x Iff"
2 x Iff"
6 x Iff"
7 x Iff"
1 x Iff"
2 x Iff"
Riyer Water
Ingestion and
Dermal Contact Risk
1 x Iff14
3 x 10"
7 x Iff14
2 x Iff"
1 x Iff"
2 x Iff11
6 x 10"
1 x Iff"
2 x 10"
3 x Iff"
3 x Iff"
1 x Iff"
2 x Iff"
6 x Iff"
Infant Breast Milk
Ingestion Risk
9 x Iff"
6 x Iff"
1 x Iff'
6 xlff7
5 xlff'
2x Iff'
3 x Iff"
4x10'
3 x Iff1"
9 x 10"
2 x Iff"
3x Iff'
NA
NA
TOTAL
CANCER
RISK'
2 x Iff"
1 x Iff10
2x Iff'
2x Iff7
1 x Iff"
4x Iff'
2 x 10"
3x Iff'
9x 10"
5 x Iff"
1 x Iff"
3 x 10'
5 x 10"
1 x 10"
Volume V
                                                                VHI-43
-------
TABLE VIII-10 (continued)
Chemical-specific Carcinogenic Risks for the
Adult Subsistence Farmer in Subarea El (Area Average)
Chemical
Soil Ingestion
and Dermal
Contact Risk
Total Meal and
Egg Ingestion'
Risk
Total Dairy
Product Ingestion*
Risk
Total Fruit and
Vegetable
Ingestion'
Risk
River Water
Ingestion and
Dermal Contact Risk
Infant Breast Milk
Ingestion Risk
TOTAL
CANCER
RISK'
Total Risks
DIOX1N TEQ
OROAN1CS TOTAL
(non-dioxin)
INORGANICS TOTAL
SUBAREA TOTAL
9 x 10"
1 x 10'°
6x ia"
i x 10'
NOTES:
* Based on ingestion of beef, pork, chicken
* Based on ingestion of milk, cheese, milk
* Based on ingestion of exposed, protected
1 Total cancer risk does not include infant b
6x ia'
i x 10'
3 x Iff10
7 x 10'
4x 1O'
2x ia'
3 x Iff"
6x W
4x10'
2x 10'
i x 10'°
5x 10'
1 x 10"
2 x 10"
2 x 10"
2 x 10"
6xl07
I xlO*
NA
2x 10*
1 x 10*
3x IOT
5 x 10'"
1 x 10«
, other poultry, and eggs
iesserts, yogurt, cream, and butter
eafy, and root produce, and exposed and protected fruit
reast milk ingestion risk
Volume V
                                                                   VIII-44
-------
TABLE VIII-1I
Chemical-specific Noncarcinogenic Hazard Indices for the
	 Adult Subsistence Fanner in Subarea El (Area Average)
Chemical
Bis(2-ethylhexyl)phthalate
Carbon tetrachloride
Di(n)octyl phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
Antimony
Arsenic
Barium
(Beryllium
Cadmium
Chromium (hexavalent)
Mercury
Nickel
Selenium
Soil Ingestion
and Dermal
Contact
HI Value
2 x ia'°
4x 10*
6 x ia"
5 x io"
6 x 10*
6x ia7
3 x ia10
2x ia7
?x ia9
4x ia7
2 x IO9
6 x 10"
3 x 10'
2x Ifr9
4x 10*
6 x 10 '°
4 x 107
Total Meat
and Egg
Ingestion*
HI Value
======
2x [0*
5 x 10"
2x 10^
6x 10*
5 x Itt7
4 x ia7
7 x ia'°
1 x IO3
8x 10*
2x 10*
7 x 10"
7 x 10"
4 x 10*
1 x 10*
1 x 10s
3 x 10*
2 x IO5
. 	 11= 	 	
Total Dairy
Product
Ingestionfc
HI Value
2x 10-*
4x ia9
2x lO*
7x 10^
3x la7
2x ia7
4 x ia10
i x ia3
3 x 10*
2x ia7
2x 1O*
2 x Itt13
7x ia9
7 x 10"
2 x 10s
6 x 109
1 x 10s
^ *'•"•' •' •^^-^•ii-i 	 I.,,.
Total Fruit and
Vegetable
Ingestion0
HI Value
*^"*^^^^^^^^^^"*"™^^^^^^^^™*'
1 x W
9x 10^
2x ia5
3 x 109
5 x 107
1 x 10*
9 x ia10
2x 10*
2 x 107
1 x 10*
3x 1041
3 x 10"
4 x 107
9 x 10 lo .
6 x lO^1
1 x 10"
2 x 10*
River Water
Ingestion and
Dermal Contact
HI Value
==^===
3 x 10"
2 x 10-"
5 x ia12
2 x 10"
8 x 10'°
8 x ia10
7 x ia13
1 x 10*
5 x 10"
2 x 10"
1 x 10 l3
1 x 10"
4x 1013
2 x 10 •'«
3x 10 In
3 x 1014
1 x 10"
=1=5= =
Total
Noncancer
HI Value
5 x \0*
9x 10^
5 x 10^
1 x 107
1 x 10*
3 x 10*
3 x 109
2 x 101
3 x 107
4 x 10*
5 x 10"
2 x 10 10
5 x 107
2 x 10"
6 x 10"
5 x 10*
4 x 10'
Volume V
                                                               VHf-45
-------
TABLE VI11-11 (continued)
Chemical-specific Noncarcinogenic Hazard Indices for the
Adult Subsistence Farmer in Subarea El (Area Average)
Chemical
Silver
Thallium
Zinc
Soil Ingestion
and Dermal
Contact
HI Value
2x ia9
7 x NT6
2 x ia'°
Total Meat
and Egg
Ingestion"
HI Value
7 x 10*
7 x 10^
\ x 10'
Total Dairy
Product
Ingestionb
HI Value
2 x 10*
3 x 105
7 x 10'°
Total Fruit and
Vegetable
Ingestion"
HI Value
1 x 107
2x 10*
1 x 107
River Water
Ingestion and
Dermal Contact
HI Value
1 x 10"
8 x 10"
2 x 10'"
Total
Noncancer
HI Value
2 x 10*
7 x 10*
1 x 107
Total Hazard Indices
ORGAN1CS TOTAL
(non-dioxin)
INORGANICS TOTAL
SUBAREA TOTAL
1 x 10*
1 x 10'
1 x 10'
1 x 101
7 x 10^
2x 10'
1 x 103
7 x ia5
2 x 10'
1 x 10^
ox 10^
7 x lO^1
2x 10*
4 x 10 10
2x 10*
3 x 101
1 x 101
4x 10'
Notes:
a - Based on ingestion of beef, pork, chicken, other poultry, and eggs
b - Based on ingestion of milk, cheese, milk desserts, yogurt, cream, and butter
c - Based on ingestion of exposed, protected leafy, and root produce, and exposed and protected fruit
Volume V
                                                                  Vlll-46
-------
TABLE Vm-12
Estimated Cancer Risks Due to Exposure from Direct and Indirect Pathways
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Population Subgroup
Resident
Adult
2x 10"7
5x 10"7
8x 10*
2x 10-7
3x 10*
5x10*
8x10*
3x 107
4x10*
8x 1O*
2x 10*
2x10*
1 x 1O7
3x 1O7
5x 1O*
1 x 1O7
2x 10*
4x 1O*
8x 1O*
2x 1O7
3x10*
8x 10*
1x10*
2x10*
Resident
Child
4x 1O7
1 x 10*
2x 1O7
4x 1O7
8x10*
1 x 1O7
2xlO7
7x 1O7
9x10*
2x 1O7
4x 10*
6x 1O*
3x 1O7
8x 1O7
1 x 107
3 x 107
6x 10*
9x 10*
2x 1O7
5x 1O7
8x 10*
2x 107
3x 10*
5x 10*
Farmer
Adult
6x 1O7
2x10*
3xl07
6xl07
IxlO7
2xl07
3xl07
1 x 1O*
1 x 107
3 x 1O7
6x 10*
9x 1O*
4x 1O7
1 x 10"
2x 107
4x 107
9x 10*
1 x 107
3 x 1O7
8x 107
1 x 1O7
3 x 1O7
5x 10*
8x 1O*
Farmer
Child
6x 107
2x10*
3x 1O7
6x 107
IxlO7
2xl07
3x 107
Ix 10*
Ix lO7
3x 107
6x 10*
8x 10*
4x 1O7
1 x 1O*
2x 107
4x 1O7
9x 1O*
1 x 1O7
3x 107
8x 1O7
1 x 1O7
3 x 1O7
5x10*
8x 10*
School-
Age Child
3x 1O7
8x 1O7
1 x 1O7
3x 1O7
5x 10*
8x 10*
IxlO7
5x 1O7
6x 10*
IxlO7
3x 1O*
4x 10*
2x 107
5x 1O7
8x 10*
2x 1O7
4x 1O*
6x 10*
IxlO7
3 x 107
5x 10*
1 x 1O7
2x10*
3x10*
Subsistence
Farmer
Adult
1 x 1O*
4x 1O6
7 x 1O7
1 x 10*
3 x 1O7
4x 1O7
7xl07
2x 1O*
3x 107
6x 107
1 x 107
2x 1O7
9x 1O7
3x 1O*
4x 107
1 x 10*
2x 107
3 x 1O7
7x 107
2x 1O*
3x 107
7x 107
1 x 1O7
2x 1O7

Subsistence
Farmer
Child
i x ID-*
4x lO"6
6 x 10"
1 x 10-6
3 x ID'7
4 x ID'7
6 x 107
2x 10-*
3 x ID'7
6 x 107
1 x ID'7
2x 1O7
9 x 107
3 x 10*
4 x 107
9x 1O7
2x 1O7
3 x 1O7
6x 107
2x 1O*
2x 107
6x 1O7
1 x 107
2x 1O7
Volume V
-------
TABLE Vm-13
Estimated Hazard Indices Due to Exposure from Direct and Indirect Pathways
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Population Subgroup
Resident
Adult
1 x 10-2
4x 10-2
6x 10-3
1 x 10-2
3x ID"3
4x 10-3
6x 10"3
2x 10-2
3x10°
6x 10-3
1 x ID"3
2x 10-3
9x 10"3
3x 10-2
4x 10-3
9x 10-3
2x 10-3
3 x ID"3
6x 10"3
2x ia2
3 x 10-3
6x 10"3
1 x 10-3
2x 10-3
Resident
Child
5x 10-2
2x 10-'
2 x 10-2
5x ID"2
1 x 10-2
2x 10-2
2x 10-2
9 x 10-2
1 x 10-2
2x 10-2
5 x 10-3
7 x lO"3
4x 10-2
1 x 10-'
2x 10-2
4x 10-2
8 x lO"3
1 x l(r2
3x 10-2
7 x 10-2
1 x 10-2
2x 10-2
4x 10-3
7 x 10-3
Farmer
Adult
1 x 10-2
4x ID"2
7x 10"3
1 x 10-2
3 x 10"3
4x 10-3
7x ID"3
3 x 10-2
3 x 10-3
7 x 10-3
1 x ID'3
2 x 10°
1 x 10-2
3 x 1
-------
TABLE Vm-14
Comparison of Average and High-End Cancer Risks and Noncancer Hazard Indices
for an Adult Subsistence Fanner in Subarea El
Exposure Pathway
Inhalation
Meat & Egg Ingestion
Dairy Ingestion
Vegetable & Fruit Ingestion
Total Cancer Risk/Hazard Index*
Subsistence Farmer
(Average)
Cancer
Risk
7x10*
7xlO-7
6x 10-7
5x 10*
1x10*
Hazard
Index
1 x 10"2
2x 10"3
2x ID"3
7x 10"
2x 10-2
Subsistence Farmer
(High-End)
Cancer
Risk
2x 10-7
3x MT6
3x 10*
3x 10-7
7x 10-*
Hazard
Index
1 x 10 :
5 x 10-'
5 x 10--'
- 2 x 10-'
2x 10-:
Notes:
« - Total oncer risk/hazard index for all exposure pathways (inhalation, food ingestion, and non-food
related pathways) combined.
Volume V
-------
TABLE Vffl-15
Comparison of Average and High-End Cancer Risks and Noncancer Hazard Indices
for an Subsistence Farmer Child in Subarea El
Exposure Pathway
Inhalation
Meat & Egg Ingestion
Dairy Ingestion
Vegetable & Fruit Ingestion
Total Cancer Risk/Hazard Index"
Subsistence Fanner
Child
(Average)
Cancer
Risk
8x 10*
3x 10-7
9x 10-7
3 x 10*
Ix 1O6
Hazard
Index
5x 10:
4x 10°
1 x 1O:
2x 10-3
7xl(r:
Subsistence Farmer
Child
(High-End)
Cancer
Risk
8x 10*
1 x 10*
3 x 10* ..
1 x 1O7
4x 10*
Hazard
Index
5 x 10":
1 x 10:
3 x 10:
6 x 10:~
1 x 10-'
Notes:
a - Total cancer risk/hazard index for all exposure pathways (inhalation, food ingestion, and non-food
related pathways) combined.
Volume V
-------
TABLE Vm-16
Input Values for the IEUBK Lead Model
Medium
Air
Air
Drinking water
Soil/dust
Soil/dust
Diet
Paint
Mother's blood
Pb cone at birth
Assumption
Background air concentration
0*g Pb/m3)
Inhalation rate (nrVday)
Background water concentration
C*g/L)
Background soil/dust concentration
(rag Pb/kg)
Soil intake (g/day)
Food intake (/tg Pb/day)
Paint intake (fig Pb/day)
Blood concentration (jig Pb/dL)
Default Value*
0.1
0 - 1 yr 2.0
1 - 2 yr 3.0
2 - 3 yr 5.0
3 - 4 yr 5.0
4 - 5 yr 5.0
5 - 6 yr 7.0
6 - 7 yr 7.0
4
200
0 - 1 yr 0.085
l-2yr 0.135
2-3yr 0.135
3-4yr 0.135
4-5yr 0.100
5 - 6 yr 0.090
6 - 7 yr 0.085
0 - 1 yr 5.53
1 - 2 yr 5.78
2 - 3 yr 6.49
3 - 4 yr 6.24
4 - 5 yr 6.01
5 - 6 yr 6.34
6 - 7 yr 7.00
0.0
2.50
Value Used
0.065'
16C
default
default
default
default
default"
default
a - USEPA 1994d.
b - OEPA 1993.
c - This auetsment.
d - Although residence! in this area may have lead anociated with the paint, this source of lead is not considered. However,
because lead emissions from the stack has no affect on the distribution of blood lead levels in local children, as discussed
in the text, this assumption doea not affect the results of this assessment.
Volume V
                                                   VTTT.<;I
-------
TABLE Vm-17
Estimated Total Cancer Risks and Hazard Indices for Subsistence Fishing
(Average for Subarea and Location of Maximum Concentration)
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Total Cancer Risk
River
Ohio River
2x 10*
3x 10*
Ohio River
6x 10-'
1 x 10*
Ohio River
2x 10-"
2x 10-'
Ohio River
2x 10*
5x 10*
NA
NA
NA
NA
NA
NA
Ohio River
2x 10*
6x 10*
Ohio River
3 x 10*
6 x 10*
NA
NA
Little Beaver Creek
2x 10*
5 x 10*
NA
NA
Tomlinson Run Lake
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
3 x 10*
NA'
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Hazard Index
River
Ohio River
5x HT
1 x 10-'
Ohio River
2x IV
4x 10"."
Ohio River
6 x ID'5
1 x 10"1
Ohio River
7x 10-*
2x 10-3
NA
NA
NA
NA
NA
NA
Ohio River
8 x lOr*
2x 10-'
Ohio River
8 x 10*
2x 10-3
NA
NA
Little Beaver Creek
2x 10"3
4 x 10-3
f^
NA
NA
Tomlinson Run Lake
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
4 x 10 '
NA'
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
s
NA
NA
a - The location of maximum concentration is not located on or near the lake
Volume V
-------
TABLE Vm-18
Estimated Total Cancer Risks and Hazard Indices for Deer Hunting
(Average for Subarea and Location of Maximum Concentration)
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Ml
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Total Cancer Risk
1 x 10*
3x10*
5x 109
1 x 10*
2x 10*
3x 1O*
5x10*
2x10*
2x 10*
5x10*
1 x 10*
1 x 1O*
7x 10*
2x 10*
3 x 10*
7x 10*
2x 10*
2x 10*
5x 10*
1 x 1O*
2 x 10*
5 x 10*
9 x 10-'°
1 x 10*
Hazard Index
5 x ID'5
1 x 10^
2 x 10J
3 x ID'5
7 x 10*
1 x 1O5
2xlO-5
8x 105
6x 10*
1 x lO"5
3 x lO*
4x 10*
3x 10-5
6x lO"5
1 x 10-5
2x ID"5
5x 10*
5x 10*
2x 1O5
7x 10"3
8x 10*
2x 105
4x 10*
^ 6 x 10*
Volume V
-------
TABLE Vm-19
Estimated Total Cancer Risks and Hazard Indices for Consumption of Fruits and
.Vegetables from Residential Home Garden
(Average for Subarea and Location of Maximum Concentration)
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Total Cancer Risk
6x 10"
2x 10-*
3x 10-'
6x 10-'
1 x 10"9
2 \ 10-'
3 x IV
1 x 10*
1 x 10*
3 x 10*
6 x 10-'°
8 x 10-'°
4x 10-9
1 x 1O*
2x 10-'
4 x 10-'
9 x 10-'°
1 x 10-'
3 x 10-'
7 x 10-'
1 x ID"9
3 x 10-'
5 x 10"10
7 x 10-'°
Hazard Index
1 x 10-
4x 10-
7 x 10-5
2x 10-
3 x 10-5
5 x lO'5
7x 10-5
3 x 10-
3 x 10-3
7 x 10-5
1 x 10-5
2 x 10'5
1 x 10-
3 x 10-
5x 10-5
1 x 10-
2x 10-5
3 x lO'5
7 x 10"5
2x 10-
3x lO"5
7 x 10'5
•"1 x lO'5
2 x lO'5
Volume V
-------
TABLE Vm-20
Estimated Cancer Risks for Infant Ingestion of Breast Milk
(Average for Subarea and Location of Maximum Concentration)
Subarea
El
Area Average
Maximum Location
E2
Area Average
Maximum Location
E3
Area Average
Maximum Location
SI
Area Average
Maximum Location
S2
Area Average
Maximum Location
S3
Area Average
Maximum Location
Wl
Area Average
Maximum Location
W2
Area Average
Maximum Location
W3
Area Average
Maximum Location
Nl
Area Average
Maximum Location
N2
Area Average
Maximum Location
N3
Area Average
Maximum Location
Cancer Risk for Infants of:
Resident
4x ID"7
1 x 1O*
2x 10"7
4x ICr7
7x 1O*
1 x 10-7
2x ID"7
7x ID"7
8x 10*
2x 10"7
3 x 10*
5x 10*
3 x ID"7
7 x 1O7
1 x 10-7
2 x 10-7
5 x 10*
7 x 10s
2x 107
5 x 107
7x 108
2x 107
3 x 10*
5x 10*
Farmer
7x 1O7
2x 10*
3x 1O7
6x 1O7
Ix 107
2xl07
3x 1O7
1 x 1O6
1 x 1O7
3x 107
6x 10s
9x 1O*
4x 1O7
1 x 1O*
2x 1O7
4 x 1O7
9x 10*
1 x 1O7
3 x 1O7
1 x 10*
1 x 1O7
3 x 1O7
6x 1O*
9x 1O*
Subsistence Farmer
2 x 10*
5 x 10*
7 x 10-"
2 x 10*
3 x 107
5 x lO'7
8 x 10-7
3 x 10*
3 x 107
7 x 10-7
1 x 107
2 x 10-7
1 x 10*
3 x 10*
5 x 107
1 x 10*
2 x 107
3 x 1O7
8 x 107
2x 10*
3 x 1O7
8 x ID'7
1 x lO'7
2 x 1O7
Volume V
-------
TABLE VI1I-21
Estimated Subarea Population Age Distributions for Residents and Fanners
Estimated Number of Residents with Gardens
Subgroup
Infants
Child
Adults
El
3
34
164
E2
8
95
459
E3
18
232
1,130
Nl
7
83
401
N2
28
332
1,615
N3
50
605
2,961
SI
2
36
187
S2
10
142
722
S3
16
225
1,138
Wl
7
79
380
W2
25
317
1567
W3
31
405
1,945
Estimated Number of Residents without Gardens
Subgroup
Infants
Child
Adults
El
6
79
383
E2
18
222
1,071
E3
42
541
2,636
Nl
16
194
937
N2
64
777
3,769
N3
116
1,412
6,908
SI
6
84
435
S2
23
330
1,685
S3
37
524
2,656
Wl
15
184
887
W2
58
740
3,656
W3
73
945
4,539
Estimated Number of Farmers
Subgroup
Infants
Child
Adults
El
0
2
14
E2
1
8
39
E3
2
20
97
Nl
1
8
34
N2
2
28
138
N3
4
52
253
SI
0
3
16
S2
1
12
62
S3
1
19
97
Wl
1
6
33
W2
2
27
134
W3
3
34
166
Source: Values estimated based on population data for ZIP coded in vicinity of the WTI facility (CACI 1991).
Volume V
                                                                   Vlll-56
-------
TABLE VIII-22
Summary of Total Estimated Cancer Risks (Direct and Indirect) for Residents and Fanners
Total Estimated Cancer Risks for Residents with Gardens
Subgroup
Infants
Child
Adults
El
5 x 107
4 x 107
2 x 107
E2
2x 1(T7
2x la7
8x 10*
E3
9 x 10"
8 x 10"
3 x 10"
Nl
2 x 107
2 x 107
8x 10"
N2
9 x 10"
8 x 10"
3 x 10"
N3
4 x 10"
3 x 10"
1 x 10"
SI
2x la7
2 x 107
8 x 10"
S2
9 x 10"
9x 10"
4x 10"
S3
4x 10"
4x 10"
2x 10"
Wl
3 x 107
3 x 107
1 x 107
W2
1 x 107
1 x 107
5 x 10"
W3
6 x 10"
6 x 10"
2x 10"
Total Estimated Cancer Risks for Residents without Gardens
Subgroup
Infants
Child
Adults
El
5 x 107
4 x 107
2 x 107
E2
2 x 107
2 x W
8 x 10"
E3
9 x 10"
8 x 10"
3 x 10"
Nl
2 x 107
2 x 107
8 x 10"
N2
9 x 10"
8x 10*
3 x 10"
N3
4 x 10"
3 x 10"
1 x 10"
SI
2 x 107
2 x 107
8x 10"
S2
9x 10"
9x 10"
4 x 10"
S3
4x 10"
4 x 10"
2 x 10"
Wl
3 x 107
3 x 107
1 x 107
W2
1 x 107
1 x 107
5 x 10»
W3
6 x 10"
6 x 10*
2 x 10"
Total Estimated Cancer Risks for Farmers
Subgroup
Infants
Child
Adults
El
8 x 107
6 x 107
6 x 107
E2
3 x ia7
3 x 107
3 x ia7
E3
1 x 107
1 x 107
1 x 107
Nl
4 x 107
3 x 107
3 x 107
N2
1 x 107
1 x 107
1 x 107
N3
6 x 10"
5 x 10"
5x 10"
SI
3 x 107
3 x 107
3 x 107
S2
1 x 107
1 x 107
1 x la7
S3
7 x 10"
6x 10"
6x 10"
Wl
5 x 107
4 x 107
4 x 107
W2
2 x 107
2x 107
2 x 107
W3
1 x 107
9 x 10"
9 x 10"
Source: Summary of area average risks presented in Table VIII- 10.
Volume V
                                                                   VIII-57
-------
TABLE VIII-23
Estimated Additional Cancer Cases Due to WTI Facility Emissions
Estimated Additional Cancer Cases for Residents with Gardens
Subgroup
Infants
Child
Adults
Total
El
1 x 10*
1 x 103
3 x 105
4x ia3
E2
2 x 10*
2x ia3
4 x 10s
6 x ia5
E3
2x 10*
2 x 10-'
4 x 103
6 x 10s
Nl
2x 10*
2 x 103
3 x 103
5 x 105
N2
2x 10*
3 x ia5
5 x 10s
8 x 10s
N3
2 x 10*
2 x 10s
4 x 103
6 x 103
SI
5 x 107
7 x 10*
1 x 103
2 x 105
S2
9 x 107
1 x 103
3 x 103
4 x 10s
S3
7 x 107
9 x 10*
2 x 105
3 x 103
Wl
2x 10*
2 x 103
4 x 103
7 x 10 3
W2
3 x 10*
4 x 103
8 x 103
1 x 10"
W3
2 x 10*
2 x 103
5 x 103
7 x 10-'
Total
2x 103
2x 10*
5 x 10*
7x 10*
Estimated Additional Cancer Cases For Residents without Gardens
Subgroup
Infants
Child
Adults
Total
El
3 x 10*
3 x 10'
6 x 10s
1 x \0*
E2
4x 10*
4 x 10'
8 x 10s
1 x 10^
E3
4 x 10*
4 x 10'
9 x 105
1 x 104
Nl
4 x 10*
4 x 103
7 x 103
1 x \0*
N2
5 x 10*
6 x 103
1 x \0*
2x 10^
N3
4x 10*
5 x 103
9x Itt5
1 x 10^
SI
1 x 10*
2 x 103
3 x 103
5 x 103
S2
2 x 10*
3 x 10s
6 x 103
9 x 10 3
S3
2x 10*
2 x 103
4 x SO3
6 x 105
Wl
5x 10*
5 x 10s
1 x 10^
2x 10*
W2
8x 10*
9 x 10s
2x 10^
3 x 10^
W3
5x 10*
6 x 103
1 x 10^
2x lO-'
Total
5 x 103
5 x 10^
1 x 101
2 x 101
Estimated Additional Cancer Cases for Farmers
Subgroup
Infants
Child
Adults
Total
Grand
Total
El
2 x 107
2x 10*
9x 10*
1 x 10 '
1 x \0*
E2
2 x 107
2x 10*
1 x 10'
1 x 10'
2 x \0*
E3
2 x 107
2x 10*
1 x 105
1 x 103
2 x 10*
Nl
2 x 107
2x 10*
1 x 103
1 x 103
2 x 10"
N2
3 x 107
3 x 10*
2x ia5
2 x 10J
3 x 10"
N3
3 x 107
2x 10*
1 x 103
2 x 103
2 x I04
SI
7 x 10*
9 x 107
5 x 10*
6 x 10*
8 x 103
S2
1 x 107
2x 10*
8x 10*
1 x 103
1 x 104
S3
9 x 10»
1 x 10*
6x 10*
7 x 10*
\ x 10"
Wl
3 x 107
3 x 10*
1 x 10s
2 x 103
2 x 10"
W2
5 x I07
5 x 10A
3 x 105
3 x 103
5 x 10"
W3
Total
3 x 107 1 3 x 10*
3 x 10*| 3 x 10 3
2x 103|| 1 x 1()4
2x I03|| 2 x I04
3 x I04 3 x 101
Source Values estimated based on population data for ZIP codes in vicinity of the WTI facility (CACI 1991) and total cancer risk (direct + ini irecl) estimates
Volume V
VIII-58
-------
TABLE Vm-24
Average Concentration Cancer Risks and Noncancer Hazard Indices for
Fugitive Organic Vapor Emission Sources at the WTI Facility
Quadrant
Adult
Child
School- Age
Child
Total Cancer Risk
Eastern
Southern
Western
Northern
8x 10-7
6x 1(T7
8x 10-7
5x 10-7
2% 10*
2x 1CT*
2x10*
1 x 10^
1 x 10*
9x 10-7
1 x 10*
8 x 10-7
Total Noncancer Hazard Index
Eastern
Southern
Western
Northern
2x 10-2
1 x 10-2
2x 10-2
1 x 10-:
7x ID"2
5x 10-2
7 x 10-2
5 x 10-=
4x ID"2
3 x 10-2
4x ID"2
3 x 10-2
Volume V
-------
TABLE Vm-25
Total Cancer Risks and Noncancer Hazard Indices at
Location of Maximum Off-site Concentration for
Individual Fugitive Emissions Sources at the WTI Facility
Fugitive Emissions
Source
Adult
Child
School- Age
Child
Total Cancer Risk
CAB System
Waste Water Tank
Truck Wash
Tank Farm
4x 10*
3 xlO*
9x 10-8
2x IO*
1 x ID"7
7x 10*
2x lO"7
4x 1O«
6 x icr8
4x 10*
1 x 10-7'
3 x 1O*
Total Noncancer Hazard Index
CAB System
Waste Water Tank
Truck Wash
Tank Farm
IxlO-3
9x ia2
3 x 10"3
5x 10-2
5x 10-3
3 x 10-'
1 x 10-5
2x ID"1
3 x ID"3
2 x 10-'
6x 10-3
1 x 10-'
Volume V
-------
TABLE Vffl-26
Area Average and Maximum Location Cancer Risks and Noncancer
Hazard Indices for Inhalation Exposure to Fugitive Ash Emissions
Quadrant
Adult
Child
School- Age
Child
Area Average
Inhalation Cancer Risk
Eastern
Southern
Western
Northern
2x 10*
1 x 10*
2x10*
1 x 10*
4x 10-*
3x10*
5x10*
3x10*
3 x 10*
2x 10*
3 x 10*
2x 10*
Inhalation Noncancer Hazard Index
Eastern
Southern
Western
Northern
1 x 10"
1 x 10"
2x 1O4
1 x 10"
5x10"
4x10"
7x 10"
4x 10"
3 x 104
2x 10"
4x 1O"
2x 10"
Maximum Location
Inhalation
Cancer Risk
Inhalation Noncancer
Hazard Index
5 x 10-7
5x 10-3
1 x 10*
2x 1O;
8 x 1O7
1 x 10:
Volume V
-------
TABLE Vm-27
Area Average and Maximum Location Cancer Risks and Noncancer
Hazard Indices for Indirect Exposure to Fugitive Ash Emissions
Quadrant
Adult
Child
School-Age
Child
Area Average
Indirect Cancer Risk
Eastern
Southern
Western
Northern
8 x 10I:
4 x 1O'2
8 x 1O'2
6 x 1O12
Indirect Noncancer Hazard Index
Eastern
Southern
Western
Northern
1 x 1O*
7x 10-7
1 x 10*
1 x 10*
4 x 10"
2 x 10"
4 x 1O"
4 x 1O"
1 x 10-"
6 x 1O':
1 x 1O"
9 x 10-':

5x 10*
3 x 1O6
5x 10*
4x 1O*
3x 1O*
1 x 1O*
3 x 10*
2x 1O*
Maximum Location
Indirect
Cancer Risk
Indirect Noncancer
Hazard Index
4 x 10-"
8x 10*
2 x 10'°
3 x 1O5
6 x 1O"
2x 1O3
Volume V
-------
TABLE VIII-28
Key Assumptions for Chapter VIII
(Risk Characterization)
Assumption
Risks for individual chemicals and exposure pathways
are summed to estimate overall risk
A resident or farmer is located at the point of maximum
impact within each subarea
The Ohio River, Little Beaver Creek, and Tomlinson
Run Lake are the main bodies of water where fishing
occurs
PAHs in fish are not evaluated because of extensive
metabolism
Noncancer health effects due to infant ingestion of
breast milk are not considered
In estimating subarea populations, even distribution of
population across a ZIP code area is assumed
Reasonable to estimated population risks because the
populations and sub-groups have been adequately
quantitated (e.g., the farming population comprises
2.5% of thd total population)
In estimating population risks, the estimated cancer risk
for children from ages 1 to 6 is applied to children
from ages 1 to 12
Basis
EPA (1989) guidance assuming no synergistic or
antagonistic effects, and assuming exposure via multiple
pathways. EPA (1986b) guidance estimates that additivity
likely when mixture components are present at low doses
and when components induce same toxic effects via same
mechanism of action.
Conservative assumption so risks at that point can be
assessed
The other water bodies in the study area that could be
used for fishing are small, privately owned ponds with
limited public access.
The literature presents data showing that PAHs are rapidly
metabolized
EPA ( 1 994a) does not include this pathway due to the
substantial uncertainty associated with it.
Reasonable assumption given lack of information on
distribution of population in ZIP code areas.
Professional judgment using site-specific data.
Professional judgment.
Magnitude
of Effect
low
high
low
low
medium
low
low
low
Direction of
Effect
overestimate
overestimate
unknown
possible
underestimate
underestimate
unknown
unknown
unknown
Notes:
low = less than a factor of two
medium = a factor of two to ten
high = greater than a factor of ten
Volume V
                                                               VIII-63
-------
TABLE Vm-29
Relative Concentrations of Selected Metals and Organic Compounds in
Cows' Milk
Substance
2,3,7,8-TCDD
Benzo[a]pyrene
Arsenic
Beryllium
Mercury
Cow Milk Concentration (mg/kg)
Based on Unit Emission Rate
1.8
3.0
5.0 x 10-
8.3 x 10-6
1.3 x 10'3
Volume V
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           M t
           e o
           M  C
           -  e
           .a  -
           <  +•
           A  U
           2  §
           ft.  |M
                                                           Cutoff
                                                           X ftbowr
                                                           X B«low
                                                           C . M»«n
                                  ie.e
                                  1 .66
                                  98 .34
                                  3 .7
        LEAD 8.99d
    6      8     IB     12     14
BLOOD  LEAD CONCENTRATION 
-------
Zlp  CODE  BOUNDARIES
 IN THE  VICINITY OF
 WT,  ItxCINERATOR FACILITY
Figure
 VIII-2
-------
c \acad\FILE_SPF_CIFlCATION
Subsistence Farmer Adult
Surrogate
Selection Cumulative
Chemical Score % of Total
Rank Cancer Risk
OCDF 1 0 6%
1, 2,3,4,6, 7,8-HpCDF 2 1 1%
1,2,3,7,8,9-HxCDF 3 29%
1, 2,3,4,7, 8-HxCDF 4 73%
1,2,3,6,7,8-HxCDF 5 152%
1,2,3,4,6,7,8-HpCDD 6 155%
2,3,4, 7,8-PeCDF 7 536%
Dibenz(a,h)anthracene 8 56 2%
1,2,3,4,7,8,9-HpCDF 9 563%
1,2,3,7,8,9-HxCDD 10 567%
2,3,4,6,7, 8-HxCDF 1 1 62 0%
1,2,3,4,7,8-HxCDD 12 630%
Benzo(a)pyrene 13 797%
1, 2,3,6, 7,8-HxCDD 14 799%
OCDD 1 5 85 9%
1,2,3,7,8-PeCDD 16 935%
lndeno(1,2,3-cd)pyrene 17 937%
1,2,3,7,8-PeCDF 18 944%
Bis(2-ethylhexyl)phthalate 19 975%
2,3,7,8-TCDD 20 98 4%
Hexachlorfcbenzene 21 98 5%
Benzo(b)fluoranthene 22 99 5%
Heptachlorobiphenyl 23 99 7%
Heptachlor 24 99 7%
2,3,7,8-TCDF 25 1000%
Hexachlorobiphenyl 27 1000%
Hexachlorobutadiene 33 1000%
Tetrachlorobiphenyl 38 1000%
Carbon tetrachloride 49 1000%




.*
(/>
aa
'o
u
o



i


. _ . — .. . .
Cumulative Cancer Risk from Incremental Addition of Chemicals)

100
90
80
70
60
50
40
30

20
10












{

/
f
'


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I




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o — -"1 1
0 3 6 9 12 15 18 21 24 27 30
Number of Selected Chemicals
COMPARISON OF SURROGATE CHEMICAL SELECTION PROCESS AND CANCER RISKS
V









Figure
VIII-3
-------
                       IX.  UNCERTAINTY ANALYSIS
A.     Introduction
       As noted in the preceding chapters, there are various sources of uncertainty and
variability throughout the risk assessment process.  These are inherent in risk assessments of
this nature and are not unique to this assessment.  Uncertainty represents incomplete
knowledge about certain parameters, and the values of the parameters, generally depend upon
model predictions or limited data.  Variability, on the other hand, represents heterogeneity
and inherent differences within a population, across geographic regions, and throughout a
given time period.  While the level of uncertainty  often can be reduced with a more complete
knowledge base, the level of variability cannot.
       The level of uncertainty present in the various phases of the risk assessment, and the
manner by which the uncertainty can be  addressed, was discussed extensively by the Peer
Review Panel, who generally agreed that a comprehensive approach was needed to quantify
the degree of uncertainty and its impact on the final risk estimates. This chapter discusses
types  and sources of uncertainty, as they apply to the risk assessment process in general and
the WTI incinerator in particular, and outlines and presents the results of a tiered approach to
uncertainty analysis for the risk assessment.

       1.     Types and Sources of Uncertainty  and Variability
             As part of the risk assessment process, risks associated with emissions from
      the WTI incinerator are estimated as a function  (f) of a number of input variables
       (x,7 • • •, xj, as follows:
                             y  =f(xltx3,  • •  •  , xk, r)                        (TX-1)

      where y represents the output variable (i.e., risk estimate). The input parameters
      include the waste composition and feed rate into the incinerator, chemical-specific
      emissions from the incinerator stack, meteorological and geological conditions,
      exposure parameters, and lexicological data.  Because some of these input parameters
      vary with time,  the risk estimate y will also be a function  of time, t.  In the context of
      risk assessment,  uncertainty analysis involves the determination of the variation or
      imprecision  in the final risk estimate that results from the  collective variation in the
      input  parameters (McKone and Bogen 1991).
Volume V                               TV.I
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              Generally, several categories of uncertainty can be identified in the risk
       assessment process—measurement uncertainty, model uncertainty, and data gaps.
       Measurement uncertainty results from inherent errors that accompany most analytic
       measurements, such as random sampling errors or systematic biases (nonrandom
       errors). Examples of parameters subject to measurement uncertainty include
       chemical-specific parameters such as Henry's constant, stack concentrations, and
       diffusion coefficients.
              Model uncertainty arises as a result of gaps in scientific knowledge or
       simplifying assumptions used in models to predict chemical and physical process
       behavior.  For example, the uncertainties associated with modeling the dispersion and
       deposition of chemical constituents must be included in the uncertainty analysis.
              Throughout the HHRA, an effort is made to use chemical- and site-specific
       data wherever possible.  However, when these data are incomplete or not available,
       default assumptions or generic/surrogate data are used to compensate for these data
       gaps.  This introduces additional uncertainty into the risk assessment.   For example,
       site-specific data are used for crop yields and meteorological conditions, but
       nationwide data are used to estimate food intake rates. The range of values for
       certain chemical and physical properties of 2,3,4,7,8-PeCDF, such as the
       vapor/particle partitioning factor, is estimated from measured values for other PeCDF
       congeners or other dioxin and furan  congeners.
             In addition to these categories of uncertainty, another issue that must be
       addressed is variability—across space, in time, and among individuals. Variability
       occurs when a quantity that could be described as  a single value consists in reality  of
       a distribution of values depending  on time, location, or other factors (Hoffman and
       Hammonds 1994; Finkel 1990).  For this risk assessment, variability is encountered
       when describing emission rates and composition, exposure populations and scenarios,
       and human susceptibility to adverse health effects, among other processes.  Examples
       of parameters that have variable quantities include body  weight and food intake rates.

       2.     Uncertainty and the Risk  Assessment Process
             The need to address uncertainty in risk assessment is discussed in the 1983
       National Research Council (NRC) report Risk Assessment in the Federal Government
       (NRC 1983), which states that:
                                                                  »"
             "The dominant analytic difficulty [in decision-making based on
             risk assessments]  is pervasive uncertainty....there  is often great
             uncertainty in estimates of the types, probability, and magnitude

Volume V                                TV *>
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              of health effects associated with a chemical agent, of the
              economic effects of a proposed regulatory action, and of the
              extent of current and possible future human exposures."

        Expanding on this general statement, NRC (1994) identifies generic sources of
        uncertainty and uncertainty-related issues to be addressed at each step of the risk
        assessment process:

              •      Hazard Identification: What do we know about the capacity of an
                     environmental agent for causing cancer or other adverse effects in
                     laboratory animals and in humans?

                     >•     The nature, reliability, and consistency of the particular studies
                           in humans  and in laboratory animals;

                     >     The available information on the mechanistic basis  for activity;
                           and

                     »•     Experimental animal responses and their relevance  to human
                           outcomes.

              •     Dose-Response Assessment:  What do we know about the biological
                    mechanisms and dose-response relationships underlying any effects
                    observed in the laboratory or epidemiology studies providing data for
                    the assessment?

                    >      The relationship between extrapolation models selected and
                           available information on biological mechanisms;

                    >•      The basis for selecting interspecies dose scaling factors to
                           account  for scaling dose from experimental animals to humans;
                           and

                    *      Correspondence between the expected route(s) of exposure and
                           the exposure route(s) utilized in the hazard studies,  as well as
                           the interrelationships of potential  effects from different exposure
                           routes.
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              •     Exposure Assessment:  What do we know about the paths, patterns,
                    and magnitudes of human exposure and number of persons likely to be
                    exposed?

                    *•      The basis for the values and input parameters used in each
                           exposure scenario;

                    »>      The major factor(s) thought to account for the greatest
                           uncertainty in the exposure estimate,  due to either sensitivity or
                           lack of data; and

                    >      The link of the exposure information to the risk descriptors
                           (e.g., highly exposed or highly susceptible groups or
                           individuals).

              •     Risk Characterization:  What are the strengths and limitations of the
                    assessment?

                    +      Descriptive information summarizing the assumptions and
                           uncertainties  that are associated with the numerical estimates of
                           risk; and

                    *•      Consideration of alternative approaches involves examining
                           selected plausible options for addressing a given uncertainty.

             In order to determine how these general types and sources of uncertainty apply
       specifically to the HHRA, the processes of chemical transport from the incinerator to
       human receptors must be evaluated in greater detail. Each process step is
       accompanied by a body of data and specifically developed models.   These processes
       and potential sources  of uncertainty include the following:

             •     Source Emissions—Data from trial burns, quarterly performance tests,
                    and predicted waste  feed information are used as the primary basis  for
                    estimating the source emissions.  Because these data may not
                    necessarily represent long-term emissions from the WTI incinerator,
                    and are subject to  fluctuations in feed composition and quantities and
                    incinerator operation, the emission rate and stack gas composition can
Volume V
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                     be uncertain and variable.

              •      Atmospheric Dispersion and Deposition— Once substances have been
                     emitted to the atmosphere, their transport and dispersion to receptor
                     sites will be dictated by meteorological conditions, physical and
                     chemical processes, and land use and geological conditions.   Since
                     many of the heavy metals of concern are particle-bound, their wet and
                     dry deposition rates will depend on the size distribution of the emitted
                     paniculate matter. The degree of uncertainty introduced into the risk
                     assessment will  depend on the accuracy of dispersion models and the
                     quality of the input data (e.g., wind speed  and direction, vapor/particle
                     partition factor)  used.

              •      Intermedia Transfer— Additional models are necessary to determine the
                     fate of atmospheric materials that deposit to the ground
                     surface— including direct deposition to crop plants and deposition to
                     surface soils and waters, with subsequent transport in environmental
                     media and incorporation in the food chain. These models rely upon
                     numerous site- and chemical-specific parameters,  including site-specific
                     parameters such as crop yields and  soil properties, and chemical-
                     specific parameters such as soil/water distribution coefficients and soil
                     degradation rates. The uncertainty  resulting from the use of these
                     models depends  on the quality of the data used for these parameters.

              •      Human Exposure Patterns— Numerous assumptions are required to
                     estimate direct exposure via inhalation of ambient air, and indirect
                     exposures through food and drinking water intake. There is uncertainty
                     and variability associated with individual behavior patterns and the
                     exposure factors used in the assessment.  While some nationwide
                     surveys are available to characterize the general variability in human
                     behavior patterns, uncertainty is introduced when applying these data to
                     a certain subpopulation  of interest.

              •      Dose-Response Relationships— In most cases, toxicity factors  for
                     assessing  human health  risk must be derived from laboratory animal
                     studies.  Even when data on actual human responses  to chemical
                     exposures are available, these data usually correspond to high dose
Volume V
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                    conditions and must be extrapolated to the lower doses more typical of
                    routine environmental exposures. The reliance on toxicity data from
                    animal studies or high dose human exposures introduces additional
                    uncertainty into the risk assessment.

       Each of these major potential sources of uncertainty is considered in developing the
       quantitative methodology for uncertainty analysis described in this chapter.

B.     A Three-Tiered Approach to Uncertainty Analysis
       The uncertainty analysis for the risk assessment consists of three tiers, or  levels of
analysis.

       •     Tier I—Quantification and analysis of input parameter variances
             Where possible, input parameters used in the risk assessment are accompanied
             by the estimation error or the experimental standard deviation associated with
             the parameters. A summary and justification of the assumptions used for each
             input parameter range are included.

       •     Tier n—Sensitivity analysis
             This analysis assesses how model predictions are affected by model reliability
             and data precision.  The  goal of a sensitivity analysis is to rank the input
             parameters on the basis of their contribution to variance in the output.

       •     Tier HI—Variance propagation
             This final tier involves quantifying how the overall accuracy of risk estimates
             is related to the variability and uncertainties associated  with the models, inputs,
             and exposure scenarios.

Recent examples of applications of this type of approach to uncertainty  in risk assessment
include the estimation of human health  risks associated with exposure to hexachlorobenzene
and benzo(a)pyrene (BaP)  through the consumption of homegrown food (McKone 1994);
exposure to perchloroethylene (PCE) in California ground water (McKone and Bogen  1991);
risks to children playing in soils contaminated with benzene and BaP  (Thompson  et al.  1992);
and carcinogenic health risks due to the emissions of a coal-fired power plant (Seigneur et al.
                                                                   r'
1994). A more detailed description of  each tier and the associated implications is discussed
below.
Volume V                                TV c.
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        1.     Tier I—Quantification of Input Parameter Variances
               The first tier in the uncertainty analysis quantifies ranges for the input
        parameters,  reflecting uncertainties and variances in their values. For those
        parameters that are experimentally determined, the experimental standard deviation is
        provided.  Other parameters that are calculated from regression equations are
        accompanied by the standard error of the estimator.
               Associated with the fate and transport models are a number of partition and
        biotransfer factors, some of  which may be uncertain by several orders of magnitude.
        Input parameters likely to have uncertainty factors greater than a factor of five include
        octanol-water partition coefficients (K,^), organic-carbon partition coefficients (K^.).
        Henry's law constant (H), and steady-state biotransfer factors (Ba).  Each of these
        parameters is chemical-specific.  Available literature is used to determine appropriate
        "most likely" values and ranges for these parameters.
               The output variables from some models serve as input variables to other
        models. For each model used, an estimate is made of the uncertainty associated with
        that model.  For example, the output variables from atmospheric dispersion models
        are ambient air concentrations of the  emitted species.  These calculated concentrations
        are used to determine exposure levels at the receptor site.  Therefore,  it is necessary
        to estimate the level of accuracy of the model in order to quantify the uncertainty of
        the model  outputs.  For example, at this site,  the atmospheric dispersion model ISC-
        COMPDEP simulates atmospheric dispersion to within a factor of approximately four
        (Chapter V of Volume IV).

       2.     Tier n—Sensitivity Analysis
              Some parameters have a more  significant effect on the estimates of health risks
       calculated by the models than others.  Therefore,  to reduce the computational burden
       to a reasonable level, the uncertainty analysis focused on those influential parameters
       to which the calculated health risks  are most sensitive.   These influential parameters
       are identified through a sensitivity analysis.
              The goal of a sensitivity analysis is to rank the input variables on the basis of
       their contribution to variance  in the output.  Sensitivity analyses can  be either global
       or local. A global sensitivity  analysis quantifies the effects of variation in parameters
       over their entire range of values.  A local sensitivity analysis is used to examine the
       effects of small changes in parameter  values at some defined point in the range of
       outcome values.
              The process for identifying the influential parameters involves computing
       several dimensionless parameters for each input variable. The first required

Volume V                               TV -7
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       parameter is the local sensitivity index (LSI^, which describes the effect on a model
       output for a small perturbation in an input parameter (Seigneur et al. 1994). The
       advantage of local sensitivity analysis is the relative ease in application, since the
       range of parameter values is not required.
              It is important, however, that the model output not only be a sensim e function
       of an input variable (i.e., high LSI; values), but also that the input variable has a
       significant range of expected values to allow the input variable to influence the model
       output.  For example, if a model output exhibits strong local sensitivity to a particular
       input variable that has a relatively constant and  well known value, this  input variable
       will not be a particularly influential parameter.  Thus, to determine the global
       sensitivity of an input parameter, another dimensionless parameter that  provides a
       measure of the  expected variation of an input variable over its range of probable
       values is needed.  The coefficient of variation (CVi) is used for this purpose, and is
       calculated as follows:
       where a, is the standard deviation of the parameter distribution and Xi is the mean
       value of the input parameter x,.
             Given the assumptions of this analysis, the product of the local sensitivity
       index, LSI,, and the coefficient of variation, CV,,  is directly related to a global
       sensitivity index, GSI,, defined as follows:
                                            (Av )
                                            v   w
       where (Ay^,^ is the maximum range in risk estimates resulting from the maximum
       variation in an input parameter, and y is the risk estimate using typical values for all
       input parameters.  The result is a representative measure of the impact that an
       individual parameter may have on the risk model.  By computing and comparing
       values of GSI, for all of the input parameters, the influential parameters can be
       identified and ranked in importance of affecting the risk outcome.  This approach to
       sensitivity analysis is similar to that applied by U.S. EPA (1994b,c).
             For the influential parameters  identified, it is also useful to determine the
       probability distribution functions (PDFs) for these parameters. The PDF provides a
       measure of a parameter's central tendency and allows the estimation of extreme
       values.  Knowledge of the PDF is also useful for modeling the parameter as a random
Volume V
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       variable. While available data may be adequate to determine the shape of the PDF
       for some parameters, subjective PDFs might need to be estimated for other
       parameters bised on scientific judgment (Haimes et al. 1994).  For example.
       measured values for parameters such as partition coefficients and biotransfer factors
       generally follow lognormal distribution functions (McKone 1994). Therefore, for a
       particular chemical, if only limited data are available for characterizing distributions
       for these parameters, a lognormal PDF is assumed to apply.  For other parameters
       where only minimum, maximum, and most likely values are known, either triangular
       or uniform distributions are used (Haimes et al. 1994; Finley et al.  1994).

       3.    Tier JH—Variance Propagation
             After the input parameter variances have been determined  (Tier I) and the most
       influential parameters and their PDFs identified (Tier PI), the final step in the
       uncertainty analysis is to evaluate the combined effect of the identified uncertainties
       on the output variable (i.e., risk to human health).  Risks to human health are
       estimated using  a series of models, with the output variables from some models
       serving as input variables to other models.  The process for ascertaining the
       cumulative effect of input parameter and individual model uncertainties on the
       ultimate risk estimates is known as variance propagation.  One of the results of the
       variance propagation is a probability  distribution for the model output.  Once this
       PDF is estimated, the expected likelihood or probabilities of the risk predictions are
       known and confidence levels can be established for various levels of risk.
             A widely used variance propagation method is through Monte Carlo analysis
       (Hoffman and Hammonds 1994; Thompson et al. 1992).  In a Monte Carlo method,
       each  of the influential input parameters is represented by a PDF that defines  both the
       range of values for  the parameter and the likelihood that the parameter has a value  in
       any subinterval of that range.  The model is iterated, selecting each  member  of the
       input parameter  set  by random sampling.  Iterations are continued until a variance of
       the output can be determined.  This variance reflects the combined impact of the
       variances in the  input parameter set as propagated through the model.
             An alternative to the Monte Carlo method is Latin hypercube sampling (LHS),
       which is a modified Monte Carlo method.  LHS uses stratified random  sampling to
       ensure an even selection of input parameter values across the range of possible values.
       If the output is a monotonic function of the input, LHS has been shown to be more
       efficient than an unmodified Monte Carlo method (Iman and Helton  1988).  LHS is
       also preferable when parameter values in the low- or high-end tails of the PDF are
       important.

Volume V                                ry.q
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              In both Monte Carlo and LHS analyses, sample values for each input
       parameter generally are selected independently of the values of other input
       parameters.  However, some of the input parameters may be correlated.  For
       example, values of body weight and ingestion rates are not expected to be independent
       of each other.  For pairs of correlated variables, the random  sampling methodology
       should be modified to preserve these relationships.

 C.    Implementation of Tiered Approach to Uncertainty Analysis
       As discussed in previous chapters of this report, exposures to a variety of chemicals
 released from several on-site sources may  occur through numerous direct and indirect
 pathways.  The application of all three tiers of uncertainty analysis for all chemicals and
 every exposure pathway would be an enormous undertaking.  Therefore, a more focused
 approach is adopted for this risk assessment.
       The uncertainty analysis for the HHRA addresses source emissions,  atmospheric
 dispersion, and exposure assessment components of the risk assessment. The toxicity  criteria
 (i.e., slope factors and  reference doses) are not treated as input variables in the uncertainty
 analysis, however, because it is generally not possible to quantify the uncertainty in
 developing the criteria.  For example, the  uncertainty in developing a slope factor for  dioxins
 and furans from  laboratory animal data cannot be reliably estimated.  Furthermore, the
 uncertainty associated with the slope factor for certain dioxin and furan congeners, such  as
 2,3,4,7,8-PeCDF, is greater than for congeners that have been studied more extensively,
 such as 2,3,7,8-TCDD.
       Some of the  steps in the uncertainty analysis can be eliminated based on prior
 knowledge of the fate, transport, and toxicity of the chemicals.  For example, the greatest
 risk has been determined to occur through  indirect exposure pathways (Chapter VTfl).  In
 order for a chemical to pose a significant threat to human health via indirect exposure
 pathways, the chemical must be relatively persistent in environmental media, bioconcentrate
 in human or animal tissues, or both.  For these reasons, there are a relatively limited number
 of chemicals that contribute significantly to the risk posed by indirect exposures. Screening
 of chemicals and exposure pathways of greatest concern is performed to focus the application
 of the second and third tiers of the uncertainty analysis.
       The uncertainty analysis adopted for the HHRA consists of the following elements:

       1.     Tier I and n analyses are performed for the exposure assessment  for the
             following specific cases:

             •     The organic chemical estimated to pose the greatest carcinogenic  health

Volume V                               TY.m
-------
                     risk to the most highly exposed subgroup via indirect exposure
                     pathways (i.e., indirect exposure to 2,3,4,7,8-PeCDF by adult
                     subsistence fanners); and

              •      The metal estimated to pose the greatest carcinogenic health risk to the
                     most highly exposed subgroup via indirect exposure pathways (i.e.
                     indirect exposure to arsenic by adult subsistence farmers).

              For each of these cases, the uncertainty analysis is performed on the risks at
              the location where risk posed by the chemical is greatest.  For 2,3,4,7,8-
              PeCDF, the route of indirect exposure that poses the greatest risk is associated
              with vapor-phase uptake by vegetation. Thus, the uncertainty analysis for this
              chemical and pathway focuses on the location where vapor uptake is greatest.
              For arsenic, the greatest risk is associated with particulate-phase wet
              deposition.  Thus, the uncertainty analysis for this chemical and pathway
              focuses on the location where wet deposition is greatest.  Both of these
              locations are situated in subarea El.
                     As discussed in Chapter Vm, none of the chemicals analyzed in this
              risk assessment are determined to result in a hazard index (HI) value exceeding
              1.0, indicating a very low potential for noncancer health effects. For this
              reason, the quantitative uncertainty analysis addresses carcinogenic risk only.

       2.      A Tier I analysis is performed for the emissions characterization step and the
              atmospheric dispersion model for 2,3,4,7,8-PeCDFand arsenic,  so that
              uncertainties associated with these separate components are identified.  This
              Tier I  analysis consists of the identification of ranges for these variables and an
              estimation of the PDF.  These components are also included in the Tier n
              sensitivity analysis.

       3.      Steps 1 and 2 above are combined in a Tier HI analysis.  This consists of a
              modified Monte Carlo  (i.e., Latin hypercube sampling) simulation using the
              estimated uncertainties and variabilities for the influential parameters identified
              in the  sensitivity analysis.

       Using the approach outlined above, this focused application quantifies the
uncertainties for the chemicals and exposure pathways of greatest concern.  This approach is
consistent with EPA's recent risk characterization guidance, which recommends that

Volume V                               IX-11
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uncertainty analyses for risk assessments be focused, rather than including the evaluation and
assessment of "every conceivable exposure scenario for every possible pollutant" (U.S. EPA
1992a, 1995a).
D.    Results
       1.     Estimation of Input Parameter Ranges
              Point estimates of risk developed using typical values for each of the input
       parameters required by the model equations summarized in Chapter VI and in
       Appendix V-7 are presented in Chapter VIE.  In order to estimate the uncertainty
       associated with this risk estimate, ranges of the possible values for the input
       parameters are determined, and are summarized in Table DC-1.  The rationale for the
       selection of each of the ranges are discussed in Appendix V-21.  While ranges are
       defined based on available data or guidance to the extent possible,  scientific judgment
       is used to estimate conservative ranges where appropriate data or guidance are
       unavailable.

       2.     Sensitivity Analysis
              The next step in the uncertainty analysis is to determine which of the input
       parameters have the ability and the range in values to influence the model output.  To
       determine these influential parameters,  global sensitivity index (GSI) values are
       calculated for each input parameter using equation (TX-3).
              The results of the sensitivity analysis are summarized in Table IX-2.  The
       "primary" influential parameters  that are retained for the uncertainty propagation are
       those with an absolute GSI  greater than 0.25.  This corresponds to the parameters for
       which the range of possible output values (i.e., the range of risk estimates)  are greater
       than 25%  of the average output value (i.e., the typical risk estimate).  To determine
       whether the "primary" influential parameter retention criterion of GSI > 0.25 is
       sufficient to represent the total output variability, a group of "secondary" influential
       parameters is also selected.  This group includes parameters with GSI values between
       0.05 and 0.25.  A variance propagation using both the primary and secondary
       influential parameters  will be compared to the  results using only the primary
       influential parameters.
              The influential parameters identified in  the sensitivity analysis are summarized
       below, in order of decreasing influence:
Volume V                                TV.IO
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              Indirect exposure to 2.3.4.7.8-PeCDF
                     Primary influential parameters:
                           •     Henry's constant (H)
                           •     Octanol/water partition coefficient
                           •     Dispersion factor
                           •     Emission rate
                           •     Beef intake rate (ER^f)
                           •     Vapor/particle partitioning factor (4>)
                           •     Animal tissue bioconcentration factors (BCF)
                           •     Fraction of milk that is fat
                           •     Body weight (BW)
                           •     Fraction of beef that is fat
                           •     Milk intake rate
                           •     Diet  of beef cattle
                           •     Diet  of dairy cattle
                    Secondary influential parameters:
                           •     Pork intake rate (BR^
                           •     Leafy vegetable intake rate
                           •     Fraction of pork that is fat
                           •     Diet of hogs (DFbogJ)

             Indirect exposure to arsenic
                    Primary influential parameters:
                           •     Plant/soil bioconcentration factor (reproductive) (Br)
                           •     Beef biotransfer factor (Ba^f)
                           •     Wet deposition factor
                           •     Soil/water distribution  coefficient (KdJ
                           •     Emission rate
                           •     Beef intake rate (IR^f)
                           •     Pork biotransfer factor (Ba^
                           •     Environmental half-life on plant surfaces (t]/2)
                           •     Milk biotransfer factor
                           •     Chicken biotransfer factor
                           •     Body weight (BW)
                           •     Pork intake rate (ER^
                           •     Aboveground exposed vegetable intake rate (IRAGexpo)

Volume V                                DC-13
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                           •     Egg biotransfer factor
                           •     Leafy vegetable intake rate
                           •     Exposed fruit intake rate (JRfnpo)
                           •     Protected fruit intake rate
                    Secondary influential parameters:
                           •     Root vegetable intake rate
                           •     Diet of beef cattle
                           •     Milk intake rate
                           •     Average annual irrigation (I)
                           •     Forage crop yield (YPfonge)
                           •     Chicken intake rate (IR.^^
                           •     Aboveground protected vegetable intake rate (IRAGpr0t)
                           •     Soil intake rate (IR^a)
                           •     Plant/soil bioconcentration factor (vegetative) (Bv)
                           •     Egg intake rate (IR^,)
                           •     Average annual precipitation (P)
                           •     Average annual evapotranspiration (Ev)
                           •     Soil bulk density (BD)
       As discussed in detail in Appendix V-21, the parameters K^, and H are used for
       estimating several other parameters, including the organic carbon adsorption
       coefficient (K^):
                                logK^ = log/T^-0.21                          (IX-4)

       soil/ water distribution coefficient (Kd,):

                                  Kd = (*(0C                              (K-5)
      plant/ soil bioconcentration factor (Br):

                             logBr = 1.588-0.5781og/Tw                       (IX-6)

      root concentration factor (RCF):

                             logRCF = 0.77^^-1.52         '             (IX-7)

      and volumetric air-to-leaf biotransfer factor
Volume V
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                         logBvol = 1.0651ogJrw-log   "   -1.654                 (K-8)
                                                   [RTj

        where OC50il is the fraction of organic carbon in the soil, R is the gas constant, and T
        is the temperature. Because these five parameters are estimated using equations
        (TX-4) through (IX-8), the parameters themselves are not included in the sensitiviu
        analysis.  The uncertainty in these parameters is dependent on the uncertainty in Km
        and H,  both of which are identified as primary  influential parameters.  Thus, while
        these five parameters are not explicitly evaluated in Tiers n and HI of the uncertain!)
        analysis, they are evaluated implicitly through the inclusion of Km, and H in Tiers n
        and HI.

        3.     Variance Propagation
              For each influential parameter, the "most likely" value is assumed to be
        equivalent to its expected value, E(x), which is  also the mean, yu,  defined in terms of
        its probability distribution, p(x), as follows (Ott 1995):
                                         OB
                                E(x)  =  f x p(x) dx = n                         (TX-9)
       The probability distributions and their associated parameters are summarized in Table
       IX-3. Each parameter is modeled using one of the following three probability
       distributions:
       Lognormal:
PW
1
**tov/2T
exp
_(ln*-/ij2
2*1
                                                                               ax-io)
             where the parameters ^ and a^ are related to the mean, p, and standard
             deviation, a, by:
Volume V                                IX-I
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                                                £                           (IX-11)
                                    = exp
                                         + aL)] [exp(aL)-l]

             The geometric mean (GM) and geometric standard deviation (GSD) of x are
             expOJ and exp(0fo), respectively.
       Triangular:
                           p(x) =       -         bc
                                  (c-a)(c-b)
             where a is the minimum value of x, b is the most likely value, and c is the
             maximum value. This distribution is used primarily for parameters with
             uncertain values and little measurement data.
       Uniform:

                                    p(x)
                                            c-a
             where a is the minimum value of x, and c is the maximum value.  This
             distribution is used primarily for parameters for which a range is known and
             either no most likely value is known or the data are evenly distributed across
             the range.

             Because many physical parameters are non-negative and have been found to
      follow positively skewed distributions, the lognormal distribution is  commonly  used to
      represent such parameters (McKone 1994; CalEPA 1993; McKone and Bogen 1991;
      Finkel 1990; McKone and Ryan 1989).  Lognormal distributions are often used when
      uncertainties are expressed on a multiplicative order-of-magnitude basis (e.g., factor
      of 2).  This multiplicative uncertainty factor is related to the geometric standard
      deviation.
Volume V                              TV
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               When a likely range of values for a parameter has been specified or estimated.
        this range is assumed to represent the upper and lower bounds of a 95 percent
        confidence interval.  Thus, the possibility of the value of a parameter falling outside
        the specified range exists, but is assumed to be unlikely. For all estimated ranges.
        professional judgment is used to select a conservative estimate that corresponds to ai
        least a 95 percent confidence interval.   Specifying these upper and lower bounds  (as
        opposed to other upper and lower bounds, such as a 90th percent upper bound and a
        10th percent lower bound confidence level) allows a convenient relationship between
        these bounds and the statistical parameters of the distribution.  For a lognormal
        distribution, the geometric standard deviation relates the geometric mean (GM) with
        the upper and lower bounds of a 68 percent confidence interval (^m and ^SLB) ar|d
        the upper and lower bounds of a 95 percent confidence interval (X95UB and x9jLB)' as
        follows (Ott 1995):
                           GSD -
                                           GM
      GM
     x.
                                                        _ X61LB
(IX-15)
        Therefore, the GSD can be determined from the upper and lower bounds of a 95
        percent confidence interval (X9JUB and X95LB) as follows:
                    95LB
                              95 UB
                                     GM
GM
X6SLB
                                                      95LB
                                                               (GSD)4
ax-16)
       Similarly, for parameters for which a most likely value and an uncertainty factor are
       known (e.g., the air concentration is uncertain by a factor of four), the uncertainty
       factor (UF) is assumed to represent the square of the GSD, and the upper bound is
       estimated to be the product of the geometric  mean and the  uncertainty factor:
    'The upper and lower bounds of a 68 percent confidence intervaFcorrespond to the 84
and 16 percentile levels of the cumulative probability distribution, respectively. The upper
and lower bounds of a 95 percent confidence interval correspond to the 97.5 and 2.5
percentile levels of the cumulative probability distribution, respectively.
Volume V
                                         TV n
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                                        = (GM)(UF)                           (IX-
                       UF =
                             x,
                              95 UB
                              GM
X,
                                        95UB
GM
                               (IX-18)
       In each case, professional judgment is used to ensure this upper bound is a reasonable
       approximation of the 95th percent confidence interval upper bound.
             Most parameters in this uncertainty analysis are modeled as lognormal
       distributions; however, if appropriate data are limited to the point where variances
       cannot be estimated accurately, triangular distributions are used (Finley et al. 1994;
       Haimes et al. 1994).  Use of such a distribution does not mean that the actual
       distribution is triangular; rather, it is  used as a reasonable way to represent the
       currently available data (Finley et al.  1994; Haimes et al.  1994).
             The primary influential parameters identified in the sensitivity analysis, their
       most likely values, and PDFs are summarized below.  Estimates  of correlation
       coefficients between parameters expected to be related are also provided.  Except
       where noted otherwise, all of the following parameters are modeled as lognormal.

             a.     Indirect exposure to 2,3,4,7,8-PeCDF:

                   Henry's constant (H)
                   The Henry's Law constant of 6.2xlO~6 atm-m3/mol for 2,3,4,7,8-
                   PeCDF (U.S.  EPA 1994b), which is calculated from the chemical's
                   vapor pressure/water solubility (VP/WS) ratio (Lyman et al.  1990), is
                   used for the most likely value of H. Vapor pressures  estimated for
                   PeCDF congeners range from 1.5xlO~9 to 4.3 xl(T9  mm Hg (U.S.
                   EPA  1994b), spanning  a factor of about three.  Only one value is
                   reported for the water solubility of  PeCDFs; however, values for other
                   dioxin and furan congeners have ranges spanning about one order of
                   magnitude (U.S. EPA 1994b).  Therefore, the Henry's constant for
                   2,3,4,7,8-PeCDF is assumed to be  accurate over a factor of
                   approximately 30, which corresponds to a GSD of 2.34.  Assuming this
                   range represents the 95 percent confidence interval of a lognormal
                   distribution, the geometric mean is  estimated from equation (IX-11) to
                   be 4.4xlO~6 atm-mVmol,  with the  95 percent confidence interval
Volume V
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                    ranging from 8.0 xlO"7 to 2.4xlO~5 atm-ra3/mol.
                    Octanol/water partition coefficient
                    The only value of log K^ reported by U.S. EPA (1994b) for 2.3.4.7.8-
                    PeCDF is 6.92 (Sijm et al. 1989), which corresponds to a value for KOB
                    of 8.3 xlO6; this value is used for the most likely value of K0tt .  Values
                    have been reported for log K^, for other PeCDF congeners ranging
                    from 6.19 to 6.79 (Sijm et al. 1989).  Thus, the range of log K^
                    values for all PeCDF congeners ranges over one unit, which
                    corresponds to a range of about an order of magnitude for K^ values.
                    Because the value of log K^  for 2,3,4,7,8-PeCDF is the upper limit of
                    the range of values for all PeCDF congeners, the value of K^ for
                    2,3,4, 7,8-PeCDF is conservatively estimated to range over two orders
                    of magnitude, which corresponds to a GSD of 3.16.  Assuming this
                    range represents the 95 percent confidence interval of a lognormal
                    distribution, the geometric mean is estimated from equation (IX-11) to
                    be 4.2 xlO6 (which corresponds to a log K^ of 6.6), ranging from
                    4.2 xlO5 to 4.2 xlO7 (which corresponds to values of log Kow ranging
                    from 5.6 to 7.6).

                    Dispersion factor
                    At the point of maximum vapor uptake, the most likely value for the
                    dispersion factor for 2,3,4,7,8-PeCDF is 0.914 0*g/m3)/(g/sec).  A
                    series of sensitivity tests of the model predictions  to a range  of inputs
                    was performed to assess the response of the model to uncertainties in
                    the model input parameters (Chapter V of Volume IV). Based on an
                    analysis of these sensitivity tests and the performance of other similar
                    steady-state Gaussian models, it is estimated that the uncertainty of the
                    annual average concentration predictions from ISC-COMPDEP is a
                    factor of 4, which corresponds to a GSD of 2.  Assuming this range
                    represents the 95 percent confidence interval of a  lognormal
                    distribution, the geometric mean is estimated from equation (IX-11) to
                    be 0.72 (/ig/m3)/(g/sec), ranging from 0.18 to 2.9 (/zg/m3)/(g/sec).

                    Emission rate
                    Based on data collected duiing the February 1994 trial burn (four test
                    runs) and the 22 performance test runs conducted  between August 1993
Volume V                               TV in
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                    and August 1994, the average emission rate of 2.3,4,7,8-PeCDF is
                    4.7xl(T10g/sec, with values ranging from 9.0xlO~u to 1.5x10''
                    g/sec.  These data from the trial bum and performance tests are used to
                    determine a cumulative probability distribution for the emission rate.
                           Studies by Zacharewski et al. (1988) and Mason et al. (1987)
                    have shown selected brominated and brominated-chlorinated dioxins to
                    be comparable in toxicity to chlorinated dioxins in certain short-term
                    toxicity assays. Because EPA-approved methods for analyzing
                    brominated and brominated-chlorinated dioxins and furans are not
                    available, the presence of brominated compounds in the stack emissions
                    was not determined.  However, since brominated aromatics are not as
                    widely used as chlorinated aromatics, only a small fraction of the total
                    halogenated dioxins and furans that form during hazardous waste
                    incineration are expected to be brominated.  Based on an  initial
                    examination of the waste profiles for the first nine months of operation,
                    the amount of bromine in the waste stream is less than one-twentieth of
                    the amount of chlorine.  In order to account for the potential impact of
                    the brominated compounds, the dioxin and furan emissions are prorated
                    by an uncertainty factor in this  uncertainty analysis.  The  2,3,4,7,8-
                    PeCDF emission rate is multiplied by this uncertainty factor, which is
                    defined to have a minimum value of 1.0, a most likely value of 1.05
                    (i.e., a one-twentieth increase), and a maximum value of  1.5.  The
                    maximum value for the uncertainty factor of 1.5 reflects professional
                    judgment that brominated aromatics will not likely exceed one half of
                    the chlorinated aromatics in wnste  feeds.  Because of the lack of
                    available  data for this parameter, a triangular distribution  is assumed
                    (Finley et al. 1994).

                    Vapor/particle partitioning factor ()
                    No specific data for $ were found for 2,3,4,7,8-PeCDF.  Therefore,
                    using the theoretical approach of Bidleman (1988), the most likely
                    value for j> is estimated to  be 0.61 for 2,3,4,7,8-PeCDF . Because
                    extremely limited 2,3,4,7,8-PeCDF-specific data are available for this
                    parameter, a triangular distribution is assumed (Finley et al. 1994).
                    For the maximum and minimum values, the range of 15 measurements
                    from six studies of <£ for PeCDF congeners, 0.0 to 0.71,  is used (U.S.
                    EPA 1994b,c).
Volume, V
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                    Bioconcentration factors (BCF)
                    McLachlan et al. (1990) reported the only measured value of BCF for
                    2,3,4,7, 8-PeCDF, 3.1, which is used for the most likely value.  Values
                    are reported for other dioxin-like compounds in beef and milk fat
                    ranging from 0.05 to 5.7 (U.S. EPA 1994b; McLachlan et al. 1990:
                    Fries and Paustenbach 1990; Jensen and Hummel 1982; Jensen et al.
                    1981; Arstilla et al. 1981; Parker et al. 1980; Firestone et al. 1979).
                    with lower chlorinated congeners  generally having higher values of
                    BCF than higher chlorinated congeners.  Taking this association of
                    decreasing bioconcentration ratios with increasing chlorination into
                    consideration, the range of BCF values reported for tetra-, penta-, and
                    hexa-chlorinated dioxins and furans, from 0.73 to 5.7, is selected to
                    represent the estimated uncertainty in the BCF value for 2,3,4.7,8-
                    PeCDF in the fat content of beef, milk, pork, chicken, and eggs.
                    Because extremely limited 2,3,4,7,8-PeCDF-specific data are available
                    for this parameter, a triangular distribution is assumed (Finley et al.
                    1994).
                    Beef intake rate
                    The site-specific most likely value for IR^f is 81 g/day.  This value
                    and the cumulative distribution function were extrapolated from a 1987-
                    88 USDA national food consumption survey (USDA 1993, 1982), as
                    summarized in Chapter VI. Based on this survey, the upper and lower
                    bounds of the 95 percent confidence interval for beef intake rates are
                    321 and 14 g/day, respectively  The ingestion rate of beef is expected
                    to be related to body weight.  To account for this relationship, a
                    correlation coefficient between IR^f and BW of 0.9 is assumed.
                    Fraction of milk that is fat
                    The most likely value for the fat content of milk is assumed to be 0.02
                    (U.S. EPA 1994b).  According to data reported by Pennington (1989),
                    the value of fat^ ranges from 0.002 (skim milk) to 0.037 (whole
                    milk).  Because the data are fairly evenly distributed across this range,
                    a uniform distribution is assumed to apply for this parameter.
Volume V
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                    Body weight (BW)
                    Data and cumulative probability distributions for adult (ages 18 to 75)
                    body weights were collected during the second National Health and
                    Nutrition Examination Survey (NHANES n), conducted between  1976
                    and 1980.  Over 20,000 individuals in the United States ranging in age
                    from 6 months to 74 years participated in this survey.  Based on this
                    survey,  the 5th and 95th percentile body weights are 52 and 97 kg.
                    respectively.  The cumulative PDF from this survey (ATHC 1994, U.S.
                    EPA 1990b) is used in this uncertainty analysis.
                    Fraction of beef that is fat
                    According to data reported by Pennington (1989), the average fat
                    content of beef (including brisket, chuck, flank, ground, ribs, round,
                    shank, short loin,  and wedge-bone sirloin) is 0.23, ranging from 0.12
                    to 0.35.  Because  the data are fairly evenly distributed across this
                    range, a uniform distribution is assumed ,to apply for this parameter.
                    Milk intake rate
                    The site-specific most likely value for IR,,^ is 184 g/day.  This value
                    and the cumulative distribution function were extrapolated from a 1987-
                    88 USD A national food consumption survey (USDA 1993, 1982), as
                    summarized in Chapter VI.  Based on this survey,  the upper and lower
                    bounds of the 95 percent confidence interval for milk intake  rates are
                    918 and 10 g/day, respectively.  The ingestion rate of milk is expected
                    to be related to body weight.  To account for this relationship, a
                    correlation coefficient between IR,^ and BW of 0.9 is assumed.
                    Diet of beef cattle (DFfor^, DF^, DF.U^, DF.J
                    For beef cattle, reported soil ingestion rates range from 1 to 18% of
                    dry matter intake, which is 1 to 15 % of total intake, with a typical
                    value of 3% (U.S. EPA 1990a, Thorton and Abrams 1983).
                    Therefore, forage, grain, and silage comprise the remaining portion of
                    the diet.  Typical total intake for beef cattle reportedly consists of 72 %
                    forage, 4% grain, and 21%  silage (U.S. EPA 1990a, Ensminger 1976).
                    Generally, soil ingestion is inversely related to the  availability of forage
             (Fries and Paustenbach 1990).  The m'gher soil ingestion rates likely occur
             under poor pasture conditions with sparse vegetation, whereas periods of lush
Volume V
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              plant growth are associated with low soil intake.  Because beef cattle often
              subsist on diets that are largely forage (Fries and Paustenbach  1990), the upper
              limit of the forage diet fraction is assumed to be 99%, with a soil diet fraction
              of 1 %, in which case the lower limits of the silage and grain diet fractions
              would both be 0%. Under poor pasture conditions or for various dietary
              considerations, the lower limit of the forage diet fraction is estimated based on
              professional judgment to be one third (33%), approximately a factor of two
              lower than the typical value of 72 %,  with the soil ingestion increasing to its
              maximum value of 15 %,  and the balance of the diet comprised of an increase
              from the most likely value in either the silage or grain fractions (i.e., either
              4% grain and 48% silage or 31 % grain and 21 %  silage). The  higher silage
              diet fraction corresponds to periods of short growing seasons and low rainfall;
              the higher grain diet fraction corresponds to periods of beef cattle fattening
              (Fries and Paustenbach  1990, NRC 1984).
                    In summary, for beef cattle, the  diet fractions are assumed to range
              from 33 to 99% forage, 1 to 15% soil, 0 to 31%  grain, and 0 to 48% silage.
              Because of the limited data availability,  triangular distributions  are assumed for
              the forage, grain, and soil diet fractions; the silage fraction  is defined by a
              mass balance with the other three diet components. To account for the inverse
              relationship between soil and forage intake, a correlation coefficient of —0.9
              between DFfoilge and DF^ is assumed.

              •     Diet of dairy cattle (DFforage, DF^, DF>a^,  DF.J
                    Dairy cattle generally do not graze to the extent that beef cattle do,
                    partly because high-producing cows are unable to meet their energy
                    requirements when pasture is their main food source (Bath et al.  1985).
                    Therefore, a 99% upper bound forage diet fraction for dairy cattle is
                    not likely.  Typical total intake for dairy cattle reportedly consists of
                    64% forage, 15% grain, and 19% silage, with the remaining 2% intake
                    being soil (U.S. EPA 1990a).
                          Reported soil ingestion rates range  from 1 to 7%  of total intake,
                    with a typical value of 1 % for  lactating dairy cows and 4 % for
                    nonlactating cattle (U.S. FJ»A 1990a,  Fries et al. 1982a). Because of
                    the low cost of pasture grass and  the high  nutritive value of grain, it is
                                                                ^j*
                    unlikely that the diets of dairy cattle are completely devoid of either
                    roughage or grain (Bath et al.  1985, NRC  1978).  Therefore, based on
                   professional judgment, the lower limits of the forage  and grain diet
Volume V
                                        TV-TS
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                    fractions are estimated to be 30% and 7%, respectively, approximately
                    a factor of two lower than the typical values.  For nutritional reasons.
                    grain does not generally exceed 50% of the total diet (Stallings 1995).
                    The maximum forage diet fraction is estimated to be 92 % by assuming
                    all other diet components are at their minimum values.  The maximum
                    silage diet fraction is estimated to be 56% by assuming forage and
                    grain are at their minimum values and soil is at its maximum value
                    (assuming soil and forage ingestion are inversely related).
                          In summary,  for dairy cattle, the diet fractions are assumed to
                    range from 30 to 92% forage, 1 to  7% soil, 7 to 50% -grain, and 0 to
                    56% silage.  Because of the limited data availability, triangular
                    distributions are assumed for the forage, grain, and soil diet fractions;
                    the  silage fraction is defined by a mass balance with the other three diet
                    components. To account for the inverse relationship between soil and
                    forage intake, a correlation coefficient of -0.9 between DFforagc and
                    DF.OJ] is assumed.

             b.     Indirect exposure to arsenic:

                    Plant/soil bioconcentration factor (Br)
                    For arsenic, Baes et  al.  (1984) report the most likely values of the
                    plant/soil bioconcentration factors for nonvegetative/reproductive
                    portions of food crops and feed plants to be 0.006. Available plant and
                    product elemental concentration data for arsenic (Baes et al. 1984,
                    Shacklette et al. 1978, Vinogredov  1959)  show values of Br ranging
                    from approximately 0.002 to 0.78.   Assuming this range the 95 percent
                    confidence interval of a  lognormal distribution, the GSD is estimated
                    from equation (DC-16) to be 4.44, and the geometric  mean is estimated
                    from equation (IX-11) to be 0.002.

                    Beef biotransfer factor (Ba^)
                    Baes et al. (1984) and Ng (1982) provided the only available estimates
                    of the ingestion-to-beef biotransfer factor for arsenic  of 0.002 day/kg,
                    which is used for the most likely value for Ba^.  The GSD of the
                    arsenic biotransfer factors was not reported, however, GSDs for other
                    elements range  from  1.3 to 3.8.  Therefore, the GSD of Ba^f for
                    arsenic is conservatively estimated to be 3.8, which corresponds to a
Volume V
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                    geometric mean of 8.2xlO~4 and values for Ba^ ranging from
                    5.7 xl(T5 to 0.012.

                    Wet deposition factor
                    At the point of maximum wet deposition, the most likely value of the
                    maximum wet deposition factor is 0.22 (g/m2-yr)/(g/sec) (Chapter D of
                    Volume IV).  The actual peak values could range to as low as one tenth
                    this value, or 0.022 (g/m2-yr)/(g/sec).  For reasons discussed in
                    Chapter IV of Volume IV, the wet deposition algorithm is likely to
                    overestimate near-field wet removal rates and, therefore, wet deposition
                    fluxes.   This is due to the use of scavenging coefficients that implicitly
                    include the effects of both below-cloud and in-cloud scavenging,
                    whereas, near the stack,  only below-cloud scavenging occurs under
                    most conditions.  To estimate an upper limit for this maximum wet
                    deposition factor, the uncertainty in the ISC-COMPDEP model (factor
                    of four) is used, which corresponds to an upper limit of 0.884 (g/nr-
                    yr)/(g/sec). However, this is considered very conservative because the
                    wet deposition algorithm is likely to have a bias toward overprediction
                    of wet deposition fluxes in the near field, where the peak deposition is
                    predicted to occur.  Because no information is available regarding of
                    the probability distribution of this parameter, a triangular distribution is
                    assumed (Finley et al. 1994).

                    Soil/ water distribution factor (KdJ
                    The most likely value for Kd, for arsenic is 200 L/kg (Baes et al.
                    1984).  This value of Kd, is estimated by Baes et al. (1984) to be
                    uncertain over three orders of magnitude, which corresponds to a GSD
                    of 5.62.  Assuming this range represents the 95 percent confidence
                    interval of a lognormal distribution, the geometric mean is estimated
                    from equation (IX-11) to be 45 L/kg, ranging from 1.4 to 1,400 L/kg.

                    Emission rate
                    The most likely value for the emission rate of arsenic is 3.7 x 10~5
                    g/sec (Chapter HI of Volume ffl).  Observed variations in the system
                                                                i*"
                    removal efficiencies (SRE) for arsenic were low,  therefore the variation
                    in the emission rate of arsenic will be primarily due  to variability in the
                    waste feed composition.  As discussed in Appendix ffl-1, the waste
Volume V                               rv
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                    feed composition could vary by as much as an order of magnitude for
                    metals.  Therefore, the arsenic emission rate is assumed to vary over
                    an order of magnitude, which corresponds to a GSD of 1.78.
                    Assuming this range represents the 95 percent confidence  interval of a
                    lognormal distribution, the geometric mean is estimated from equation
                    (DC-11) to be 2.7 xKT3 g/sec, ranging from 8.4 xlO'6 to  8.4x10"'
                    g/sec.
                    Beef intake rate
                    The same probability distribution for beef ingestion rates used for the
                    2,3,4,7,8-PeCDF uncertainty analysis is used.
                    Pork biotransfer factor
                    Belcher and Travis (1989) provided the only available estimate of the
                    ingestion-to-pork biotransfer factor for arsenic of 0.0037 day/kg, which
                    is used for the most likely value for Ba^.  Because the GSD of the
                    arsenic biotransfer factors was not reported, the value of 3.8 used for
                    the GSD of Ba^f for arsenic is assumed, which corresponds to a
                    geometric mean of 0.0015 and values for Ba^ ranging from  1 . 1 x 10"4
                    to 0.022.  Lognormal distributions have been used to represent
                    biotransfer factors by  CalEPA (1993), McKone and Ryan (1989), and
                    Ng (1982).

                    Environmental half life on plant surfaces (tJ/2)
                    The most likely value for tI/2 is assumed to be 14 days  (U.S. EPA
                    1994b,c), which is the value used by the U.S. Nuclear Regulatory
                    Commission (USNRC 1977).  Miller and Hoffman (1983) analyzed 54
                    measurements of tm from  25 studies,  covering various  categories of
                    depositing substances and vegetation growth forms.  Values for these
                    measurements range from  2.8 to 34 days, with a geometric mean of 10
                    days and a GSD of 1.7
                   Milk biotransfer factor
                   Baes et al. (1984) and Ng (1982) provided the only available estimates
                   of the ingestion-to-milk biotransfer factor for arsenic of 6.0 x 10" 5
                   day/kg, which is used for the most likely value for Ba^.  Because the
                   GSD of the arsenic biotransfer factors was not reported, the value of
Volume V
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                    3.8 used for the GSD of Ba^f for arsenic is assumed, which
                    corresponds to a geometric mean of 2.5 x 10~5 and values for
                    ranging from  1.7xlO~6 to 3.6xlO~4. Lognormal distributions have
                    been used to represent biotransfer factors by CalEPA (1993). McKone
                    and Ryan (1989), and Ng (1982).
                    Chicken biotransfer factor
                    Belcher and Travis (1989) provided the only available estimate of the
                    ingestion-to-chicken biotransfer factor for arsenic of 0.2011  day/kg,
                    which is used for the most likely value for Ba^te,.  Because the GSD
                    of the arsenic biotransfer factors was not reported, the value of 3.8
                    used for the GSD of Ba^f for arsenic is assumed, which corresponds to
                    a geometric mean of 0.082 and values for Ba^^ ranging from 0.0057
                    to 1.2.  Lognormal distributions have been used to represent biotransfer
                    factors by CalEPA  (1993), McKone and Ryan (1989), and Ng (1982).

                    Body  weight (BW)
                    The same probability distribution for adult body weights used for the
                    2,3,4,7,8-PeCDF uncertainty analysis is used.
                    Pork intake rate
                    The site-specific most likely value for IRp^ is 34 g/day.  This value
                    and the cumulative distribution function were extrapolated from a 1987-
                    88 USDA national food consumption survey (USDA 1993, 1982), as
                    summarized in Chapter VI.  Based on this survey, the upper and lower
                    bounds of the 95 percent confidence interval for pork intake rates are
                    169 and 3 g/day, respectively. The ingestion rate of pork is expected
                    to be related to body weight. To account for this relationship, a
                    correlation coefficient between ER   and BW of 0.9 is  assumed.
      The most likely values and PDFs of the secondary influential parameters are
      summarized in Appendix V-21.
             The fate and transport model is coupled with the software package ©RISK
      (Palisade Corporation, Version 3.1), which is used to perform the propagation of the
                                                               /•'
      input parameter uncertainties through the model.  A Latin hypercube sampling
      analysis is performed to estimate the uncertainties associated with the risk assessment
      of indirect exposure to 2,3,4,7,8-PeCDF and arsenic for adult subsistence farmers.

Volume V                               TY.77
-------
       The LHS model is iterated until it converges on a stable output distribution, defined
       as a change of less than 1.5% in the average percentile values, the mean of the
       distributions, and the standard deviations.
             For indirect exposure to 2,3,4,7,8-PeCDF, the maximum point estimate of risk
       to adult subsistence fanners in subarea El is 1.9xlO~6 (Chapter VEH), which is
       estimated to be at approximately  the 60th percent confidence level of the derived
       probability distribution. The statistical parameters of this distribution are:

             •      Percent Confidence Levels:
                          5th   5.8xlO~8
                          10th  1.1 xlO~7
                          25th  3.3 xlO-7
                          50th  1.2X1Q-6
                          75th  4.5 xKT6
                          90th  1.6xlO-5
                          95th  3.2 xlO'3

       Convergence to this output distribution occurred after 3,200 iterations.
             For indirect exposure to arsenic, the  maximum point estimate of risk to adult
       subsistence farmers in subarea El is 9.9xlO~9, which is estimated to be at
       approximately the 70th percent confidence level of the derived probability
       distribution.  The statistical parameters of this distribution are:

             •      Percent Confidence Level:
                          5th   7.2 xlO-10
                          10th  1.1 xlO-9
                          25th  2.4 xlO-9
                          50th  5.6 xlO-9
                          75th  1.4xlO~8
                          90th  3.0 xlO-8
                          95th  5.1 xlO-8

       Convergence to this output distribution occurred after 2,700 iterations.
             To assess the potential impact of parameters not included in the variance
                                                                •f""
       propagation, the output distribution is recalculated for 2,3,4,7,8-PeCDF and arsenic
       using both the primary and secondary influential parameters.   For the secondary
       parameters, uniform  distributions are assumed, using the ranges specified in Table IX-
Volume V
-------
        1.  The resulting output distributions for 2,3,4,7,8-PeCDF and arsenic risks do not
        differ significantly from the output distributions derived using only the primary input
        parameters.  The 50 percent confidence levels do not differ by more than 3 % for
        2,3,4,7,8-PeCDF and 3% for arsenic; the 95 percent confidence levels do not differ
        by more than 7% for 2,3,4,7,8-PeCDF and. 2% for arsenic.  The location of the
        maximum point estimates of risk in the derived probability distributions is not affected
        by the secondary input parameters.  Therefore, the parameters not included in the
        variance propagation are not expected to affect the output distributions by more than
        approximately 10%.

 £.     Major Assumptions and Limitations
        The accuracy of this uncertainty analysis is dependent on several key assumptions.
 These assumptions must be taken into consideration when determining the validity and
 limitations of the results presented in this chapter.  The major assumptions of the uncertainty
 analysis are summarized in Table DC-4.

 F.     Conclusions
       A three-tiered approach to uncertainty analysis is applied to determine the impact of
 uncertainty and variability on the HHRA.  The uncertainty analysis focuses on two of the
 chemicals and exposure pathways identified to pose the greatest carcinogenic  health risks.
 The resulting probability distributions offer a means of estimating the degree  of certainty that
 the risk will be below a particular level.  Also,  by understanding which input parameters
 have the greatest impact on the output variables, additional data gaps and research needs can
 be identified for improving the accuracy of risk assessments.
       Based on the results of this uncertainty analysis, the 95th percent confidence level
 cancer risk estimate for indirect exposures to 2,3,4,7,8-PeCDF for the subsistence farmer
 subgroup in subarea El is approximately 3 x 10~*.  This value is about 15-fold higher than
 the point estimate of risk at the point of maximum impact (1.9xlO~6), as presented in
 Chapter vm.  Accordingly, based on available information and data regarding the key input
parameters, there is only a small probability that cancer risks to 2,3,4,7,8-PeCDF through
indirect exposure pathways for subsistence farmers in subarea El  are greater than 3xlO~5.
Given the contribution of 2,3,4,7,8-PeCDF to overall risks through all pathways,  it can also
be concluded that it is unlikely that the  total cancer risk for subsistence farmers in subarea
El for all  chemicals combined would exceed 1 x 10~4.
       The sensitivity analysis for 2,3,4,7,8-PeCDF indicates that the'parameters  that have
the greatest influence on the cancer risk estimate for this chemical are Henry's constant (H)
and the octanol/water partition coefficient (K^,). Both of these parameters are used for

Volume V                               TY.^Q
-------
 estimating the values of other parameters, such as the root concentration factor (RCF).
 soil/water distribution coefficient (Kd,), and volumetric air-to-leaf biotransfer factor (Bvol),
 among others.  The primary influence of H on the risk estimate is through the estimate of
 Bvo,, which is a key parameter for determining the vapor-phase uptake of 2.3,4,7.8-PeCDF
 into vegetation. K^ is also a key parameter for estimating Bvol, as well as determining the
 bioaccumulation potential of 2,3,4,7,8-PeCDF in animal tissue.  Therefore, the most
 effective approach to reducing the uncertainty in the risk estimate for 2,3,4,7,8-PeCDF
 would be to develop improved data for H and K^.
       Similarly, for arsenic, the 95th percent confidence level cancer risk estimate for
 indirect exposures (5.1 xlO~8) is calculated to be approximately 5-fold higher than the point
 estimate of risk at the point of maximum impact (9.9xlO~9), as presented in Chapter vm.
 Based on  the estimated 95th percent confidence level risk, it can be concluded that it is
 unlikely that indirect exposures to  arsenic would contribute significantly to overall risks
 associated with stack emissions.
       The sensitivity  analysis for arsenic indicated that the parameters that have the greatest
 influence  on the cancer risk estimate for this metal are the plant/soil bioconcentration factor
 (reproductive portion)  (Br) and the beef biotransfer factor (6^,^).  The location of maximum
 risk due to arsenic is the region  of maximum wet deposition.  Thus, Br, which determines
 the bioconcentration of arsenic in the reproductive portions of vegetation, and Ba,,^, which
 determines the subsequent biotransfer of arsenic into animal tissue, would be expected to
 have a major influence on the uncertainty in the risk estimate. Therefore, the most effective
 approach to reducing the uncertainty in the risk estimate for arsenic would be to develop
 improved  data for Br and
Volume V
-------
TABLE IX-1
Summary of Typical Values and Ranges of Input Parameters Evaluated in Sensitivity Analysis'
Input parameter
Typical Value
Range
Reference
Emissions and Atmospheric Transport
Emission rate (g/s)
Dispersion factor, Oig/m3)/(g/s)
Dry deposition factor, (g/m2-yr)/(g/s)
Wet deposition factor, (g/m2-yr)/(g/s)
Vapor/particle partition factor (<£)
Wind speed (m/s)
Air temperature (K)
•*;
Viscosity of air (g/cm-s)
Density of air (g/cm3)
2,3,4,7,8-PeCDF
arsenic
2,3,4,7,8-PeCDF
arsenic
2,3,4,7,8-PeCDF
arsenic
2,3,4,7,8-PeCDF
arsenic
2,3,4,7,8-PeCDF
arsenic
u
T
^,
P,
4.7x10-'°
3.7X10-5
0.914
0.0155
0.00515
0.00012
0.0245
0.221
0.61
1.0
4.1
293
1.82x10-"
1.20X10-1
9.0X10-" to 1.5X10-'
9.8 X10-* to 9.8x10-'
0.23 to 3.66
0.0039 to 0.062
0.00103 to 0.026
2.4x10-' to 6.0 X 10-"
0.00245 to 0.098
0.0221 to 0.884
0.0 to 0.71
1.0
1 to 10
265 to 301
1.68X10-" to 1.86X10""
1.18x10-' to 1.33X1Q-1
Chapter HI of Volume III
Chapter HI of Volume III
Chapter V of Volume IV
Chapter V of Volume IV
Chapter IV of Volume IV
Chapter IV of Volume IV
Chapter IV of Volume IV
Chapter IV of Volume IV
Bidleman (1988);
U.S. EPA (1994b,c)
Chapter V of Volume IV
Vreeland (1994)
USDA SCS (1968, 1974,
1981, 1982, 1983, 1989);
USDOC (1993)
Perry and Green (1984)
Perry and Green (1984)
Soil Concentration
Soil bulk density (g/cm3)
BD
1.31
1.10 to 1.55
USDA SCS (1982, 1983,
1989)
Volume V
                                                IX-31
-------
TABLE IX- 1 (continued)
Summary of Typical Values and Ranges of Input Parameters Evaluated in Sensitivity Analysis"
Input parameter
Organic carbon fraction in soil
Average annual precipitation (cm/yr)
Average annual irrigation (cm/yr)
Average annual runoff (cm/yr)
Average annual evapotranspiration (cm/yr)
Soil volumetric water content (mL/cm1)
Enrichment ratio
Erosivity factor
Erodability factor (yr"')
Slope length factor
Cover management factor
Supporting practice factor
oc^
P
1
RO
Ev
e,
E
R
K
LS
C
P,
Typical Value
0.013
95
28
25
44
0.25
3
125
0.34
0.179
0.3
1.0
Range
0.010 to 0.016
87 to 101
11 to 40
12 to 38
30 to 45
0.10 to 0.30
1 to 5
50 to 400
0.15 to 0.49
0.1 to 2.0
0.1 to 1.0
1.0
Reference
USDA SCS (1968, 1974,
1981, 1982, 1983, 1989)
USDA SCS (1982, 1983,
1989)
Jarrett (1994)
Geraghty et al. (1973)
Geraghty et al. (1973)
Seibert (1994);
U.S. EPA (1993a)
U.S. EPA (1994b,c, 1993a)
Moyer (1994);
U.S. EPA (1994b,c, 1993a)
USDA SCS (1982, 1983,
1989)
U.S. EPA (1994b,c, 1993a)
U.S. EPA (1994b,c, 1993a)
U.S. EPA (I994b,c, 1993a)
Constituent Concentrations in Meat, Eggs, and Milk
Soil bioavailability
Fraction of beef that is fat
Fraction of milk that is fat
Fs
fa**
fcUi
0.65
0.23
0.02
0.5 to 0.8
0.12 to 0.35
0.002 to 0.04
U.S. EPA (I994b,c)
Pennington (1989)
U.S. F.PA (1994b,c);
Pennington (1989)
Volume V
IX-32
-------
TABLE IX-1 (continued)
Summary of Typical Values and Ranges of Input Parameters Evaluated in Sensitivity Analysis*
Input parameter
Fraction of pork that is fat
Fraction of chicken that is fat
Fraction of eggs that is fat
Diet of beef cattle
(kg DW/day)
Diet fraction of beef cattle
Diet of dairy cattle
(kg DW/day)
».
Diet fraction of dairy cattle
grain
forage
silage
soil
grain
forage
silage
soil
grain
forage
silage
soil
grain
forage
silage
soil
fatpork
f«t**n
fat
-------
TABLE IX-1 (continued)
Summary of Typical Values and Ranges or Input Parameters Evaluated in Sensitivity Analysis*
Input parameter
Diet of hogs (kg DW/day)
Diet fraction of hogs
Diet of chicken (kg DW/day)
Diet fraction of chicken
grain
silage
soil
grain
silage
soil
grain
soil
grain
soil
QP,™
QP.i^
QP»a
DF^
DF.....
DF^
QP^u,
QP.OU
DF^
DF^
Typical Value
3.0
1.3
0.34
0.65
0.28
0.07
0.08
0.0024
0.97
0.03
Range
1.5 to 3.4
0.84 to 2.8
0.086 to 0.34
0.33 to 0.78
0.18 to 0.64
0.02 to 0.07
0.080 to 0.087
0.0 to 0.0024
0.97 to LOO
0.00 to 0.03
Reference
U.S. EPA (I993a);
Fries and Paustenbach (1990);
NRC (1988);
Fries et al. (1982b)
U.S. EPA (1993a)
Vegetation Concentration
Crop yield, above ground exposed
vegetables (kg DW/m2)
Crop yield, leafy vegetables (kg DW/m2)
Crop yield, forage (kg DW/m2)
Crop yield, silage (kg DW/m7)
Fraction of wet deposition that adheres to
plant surface
Length of exposure to deposition, exposed
vegetables (yr)
YPM5e,po
YPW
YPforap=
Yp.lhr
Fw
' PAOoipo
0.09
0.18
0.449
2.989
0.60 (organics)
0.46 (metals)
0.226
0.01 to 0.25
0.09 to 0.35
0.29 to 0.57
2.5 to 3. 4
0.32 to 0.79
0.32 to 0.60
0.123 to 0.329
Belcher and Travis (1989)
Belcher and Travis (1989)
USDC (1993a,b,c)
USDC (1993a,b,c)
U.S. EPA (I995c);
Hoffman et al. (1992)
PDA (1994)
Volume V
IX-34
-------
TABLE IX- 1 (continued)
Summary of Typical Values and Ranges of Input Parameters Evaluated in Sensitivity Analysis"
Input parameter
Length of exposure to deposition, leafy
vegetables (yr)
Length of exposure to deposition, forage
(yr)
Length of exposure to deposition, silage
(yr)
Environmental half life on plant surfaces
(days)
Tpwr
Tprofii^
Tp.ib,c
l.n
Typical Value
0.288
0.315
0.082
14
Range
0.247 to 0.329
0.27 to 0.36
0.042 to 0.1 22
2.8 to 34
Reference
PDA (1994)
PDA (1994)
PDA (1994)
Fries and Paustenbach (1990);
Miller and Hoffman (1983)
Dose
Beef intake (g/day)
Milk intake (g/day)
Pork intake (g/day)
Chicken intake (g/day)
Egg intake (g/day)
Above ground exposed vegetable intake
(g/day)
Above ground protected vegetable intake
(g/day)
Leafy vegetable intake (g/day)
Root vegetable intake (g/day)
Exposed fruit intake (g/day)
Protected fruit intake (g/day)
IRbeef
«-*
iRpo*
'Rchictn
l^
IRA(v^x>
"^AOpnX
IR,e,f
IR™*
IRFc,po
'Rppn*
81
184
34
48
22
68
33
27
78
58
79
14 to 321
10 to 918
3 to 169
9 to 164
4 to 77
1 1 to 330
5 to 160
4 to 130
12 to 380
9 to 279
12 to 386
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (1993, 1982)
USDA (199.1, 1982)
Volume V
IX-35
-------
TABLE IX-1 (continued)
Summary of Typical Values and Ranges of Input Parameters Evaluated in Sensitivity Analysis"
Input parameter
Soil intake (g/day)
Body weight (kg)
IR»u
BW
Typical Value
0.063
70
Range
0.025 to 0.100
52 to 97
Reference
LaGoy (1987)
AIHC (1994);
U.S. EPA (1990b)
Chemical-Specific Parameters: 2,3,4,7,8-PeCDF
Octanol/waler partition coefficient
Henry's constant (atm-mVmol)
Animal tissue bioconcentration factor
Soil degradation (yr~')
Diffusiviry in air (cmVs)
K™
H
BCF
%
ksg
D.
8.3 xlO6
6.2X10-'
3.1
0.0693
0.05
4.2X105 to4.2xl07
8.0xlO-7to2.4xlO~3
0.73 to 5.7
0.0347 to 0.139
0.023 to 0. 10
U.S. EPA (I994b,c);
Sijm et al. (1989)
U.S. EPA (1994b,c)
U.S. EPA (1994b,c);
McLachlan et al. (1990)
U.S. EPA (1994b,c)
U.S. EPA (1994b,c);
Thibodeaux (1979)
Chemical-Specific Parameters: Arsenic
Soil/water distribution coefficient (L/kg)
Plant/soil bioconcentration factor
Root concentration factor
Beef biotransfer factor (day/kg)
Milk biotransfer factor (day/kg)
. Pork biolransfer factor (day/kg)
Kd,
Bv (leafy)
Br (all others)
RCF
Ba^,
Ba^
BV>
200
0.04
0.006
0.008
0002
6.0xlO~5
0.0037
6.3 to 6,300
0.013 to 0.12
0.002 to 0.0 18
0.0025 to 0.025
0.0002 to 0.02 :
6.0xlO~4 to 6.0x10"'
0.00037 to 0.037
U.S. EPA (1994b,c)
Baes et al. (1984);
Shacklette et al. (1978);
Vinogradov (1959)
U.S. EPA (1994a)
Baes et al. (1984);
Ng(l982)
Baes el al. (1984);
Ng(1982)
Belcher and Iravis (1989)
Volume V
IX-36
-------
                                                           TABLE IX-1 (continued)
                         Summary of Typical Values and Ranges or Input Parameters Evaluated in Sensitivity Analysis"
                        Input parameter
                                                                Typical Value
                        Range
                               Reference
  Chicken biotransfer factor (day/kg)
                                                Bachickcn
0.2011
0.0201 to 2.01
Belcher and Travis (1989)
  Eggs biotransfer factor (day/kg)
                                                Ba.,
0.2615
0.0262 to 2.62
Belcher and Travis (1989)
Notei:
a  Parameters that were calculated from correlations (e.g.
                                                    were not included in this table.
Volume  V
                                                                  IX-37
-------
TABLE K-2
Summary of Sensitivity Analysis Results
Input Parameter*
Overall Model GS1
2,3,4,7,8-PeCDF
Arsenic
Emissions and Atmospheric Transport
Emission rate
Dispersion factor
Dry deposition factor
Wet deposition factor
Vapor/particle partition factor
Wind speed
Viscosity of air
Density of air

u
M.
P.
3.0
3.7
3.4XHT3
8.5 XNT3 -
-1.8
1.8X10-2
-7.3X10'4
8.6 X 10-"
2.4
—
1.6xlO-:'
3.9
...
...
—
—
Soil Concentration
Soil bulk density
Organic carbon fraction in soil
Average annual precipitation
Average annual irrigation
Average annual runoff
Average annual evapotranspiration
Soil volumetric water content
Enrichment ratio
Erosivity factor
Erodability factor
Slope length factor
Cover management factor
BD
oc^
P
I
RO
Ev
e.
E
R
K
LS
C
-4.9 X10-3
5.7 XIQ-5
-2.4 xlO-5
-4.9 XlO-3
0.0
2.5 XlO-5
1.8x10-'
-8.6 X 10-"
-1.7 xlO-3
-6.5 X 10-"
-5.1 XIO'3
-1.8 XlO-3
-5.6xlO-:
—
-6.6X10-2
-1.4x10''
0.0
6.0X10"2
2. 8 XlO-4
-7.0 xlO-3
-1.4X10'2
-5.3 xlO-3
-5.0X10'2
-1.6 XlO-2
Constituent Concentrations in Meat, Eggs, and Milk
Soil bioavailability
Fraction of beef that is fat
Fraction of milk that is fat
Fraction of pork that is fat
Fraction of chicken that is' fat
Fs
fcttef
faUk
fcU
Khickm
6.7 xlO-3
5.2x10-'
7.9x10^
5.4 xlO-2
1.6xlO~3
—
—
—
—
—
Volume V
rv 10
-------
TABLE K-2 (continued)
Summary of Sensitivity Analysis Results
Input Parameter*
Fraction of eggs that is fat
Diet of beef cattle
Diet of dairy cattle
Diet of hogs
Diet of chicken
fcteu,
QP^
DF_
QP
-------
TABLE K-2 (continued)
Summary of Sensitivity Analysis Results
Input Parameter*
Overall Model GSI
2,3,4,7,8-PeCDF
Arsenic
Vegetation Concentration
Crop yield, aboveground exposed vegetables
Crop yield, leafy vegetables
Crop yield, forage
Crop yield, silage
Fraction of wet deposition that adheres to a plant
surface
Length of exposure to deposition, exposed
vegetables
Length of exposure to deposition, leafy
vegetables
Length of exposure to deposition, forage
Length of exposure to deposition, silage
Environmental half life on plant surfaces
YpAOeIpo
Yp«
Ypfontje
Yp.^
Fw
TpAGsqx,
Tp,,,,
TPW
TP.^
tic
-9.6 X10-8
-8.5 xl
-------
TABLE EX-2 (continued)
Summary of Sensitivity Analysis Results
Input Parameter*
Overall Model GSI
2,3,4.7.8-PeCDF
Arsenic
Chemical-Specific Parameters
Octanol/water partition coefficient
Henry's constant
Diffusivity in air
Animal tissue bioconcentration factors
Plant/soil bioconcentration factor (vegetative)
Plant/soil bioconcentration factor (reproductive)
Root concentration factor
Beef biotransfer factor
Milk biotransfer factor
Pork biotransfer factor
Chicken biotransfer factor
Egg biotransfer factor
Soil degradation
Soil/water distribution coefficient
K^
H
D.
BCF
Bv
Br
RCF
Ba«f
Ba^
ifcw
Ba^
Ba^
ksg
Kd,
5.2
-7.3
l.lxl(T:
1.6
—
—
—
—
—
—
—
—
-1.3XKT2
—
—
...
—
—
7.2xlO-:
17
4.6 X1(T}
6.6
6.9X10'1
9.2x10-'
6.4X10"1
3.0x10-'
—
2.6
Notes:
a Ranges and typical values of input parameters used for calculating GSI nimmanzed in Table K-1 . Primary influential parameters
with GSI values in bold were included in the variance propagation.
Volume V
                                   TY.41
-------
TABLE K-3
Probability Distributions for Influential Parameters
Input Parameter
Probability Distribution
Type
Parameters"
Non-chemical specific parameters
body weight
Fat fraction in beef
Fat fraction in milk
Intake rate of beef
Intake rate of milk
Intake rate of pork
Diet of beef cattle
Diet of dairy cattle
BW
feW
fet^
IR^f
iR^
nu
MW
DF_
DF«u
ww
DF^,
DFMU
lognormal
uniform
uniform
lognormal
lognormal
lognormal
triangular
triangular
triangular
triangular
triangular
triangular
cumulative: 5%=52.3, 15%=57.6, 50%=68.7,
85% =84.4, 95% =97
a=0.12, c=0.35
a=0.002, c=0.037
cumulative: 5%=27, 25%=52, 50% = 81.
75% = 138, 90%=203, 95%=251, 99%=364
cumulative: 5 % = 20, 25 % = 87 , 50 % = 1 84 ,
75%=333, 90%=552, 95% = 712, 99% = 1.042
cumulative: 5%=5, 25% = 14, 50%=34, 75%=61,
90% =95, 95% = 127, 99% = 195
a=0.33, b=0.72, c=0.99
a=0.0, b=0.04, c=0.31
a=0.01, b=0.03, c=0.15
a=0.30, b=0.64, c=0.92
a=0.07, b=0.15, c=0.50
a=0.01, b=0.02, c=0.07
2,3,4,7,8-PeCDF
Emission rate
Emission rate
correction factor6
Dispersion factor
Vapor/particle partition
factor
Octanol/water partition
coefficient
Henry's constant
Animal tissue
bioconcentration factors

K^
H
BCF
lognormal
triangular
lognormal
triangular
lognormal
lognormal
triangular
cumulative: 5% =9x10-", 19% = 1.3xiO-'°,
34% = 1.7xlO-'°, 48%=2.7xlO-'°,
59%=4xlO-'°, 70%=5.3xlO-'°, 88% = 1.2xlO-',
95% = 1.5x10''
a=1.0, b=1.05, c=1.5
GM=0.72, GSD=2.0
a=0, b=0.61, c=0.71
GM=4.2xl06, GSD=3.16
GM=4.4X10-6, GSD=2.34'
a=0.73, b=3.1, c=5.7
Volume V
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TABLE K-3 (continued)
Probability Distributions for Influential Parameters
Input Parameter
Probability Distribution
Type
Parameters*
Arsenic
Emission rate
Wet deposition factor
Soil/water distribution
factor
Beef biotransfer factor
Milk biotransfer factor
Pork biotransfer factor
Chicken biotransfer
factor
Egg biotransfer factor
Plant/soil
bioconcentration factor
(reproductive portions)
Environmental half life
Kd.
Ba^
Ba,^
Ba^
*•**.
Ba^
Br
tin
lognonnal
triangular
lognonnal
lognonnal
lognonnal
lognonnal
lognonnal
lognonnal
lognonnal
lognonnal
GM=2.7xKT5, GSD=1.78
a=0.0221, b=0.221, c=0.884
GM=45, GSD=5.62
GM = 8.2X10~4, GSD=3.8
GM=2.5xl(T5, GSD=3.8
GM=0.0015, GSD=3.8
GM=0.082, GSD=3.8
GM=0.11, GSD=3.8
GM=0.002, GSD=4.44
GM=10, GSD=1.7
Notes:
a Lognormal distributions: GM= geometric mean, GSD=geometric standard deviation
Triangular distributions: 1= minimum, b=most likely value, c= maximum
Uniform distributions: a = minimum, c = maximum
b Emission rate of 2. 3,4,7, 8-PeCDF prorated by this correction factor to account for the presence of unmeasured brorrunated furans
Volume V
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                                                                  TABLE IX-4
                                                        Key Assumptions For Chapter IX
                                                             (Uncertainty Analysis)
                     Assumption
                           Basis
Magnitude
 of Effect
Direction of
   Effect
  The uncertainty analysis is performed for a
  population subgroup assumed to reside at the location
  of maximum impact to facility emissions.
Conservative assumption based on professional judgment.
   high
overestimate
  The uncertainty analysis is limited to two specific
  cases:  the organic chemical and the metal estimated
  to pose the greatest carcinogenic health risks to the
  most highly exposed subgroup via indirect exposure
  pathways (i.e., indirect exposure to 2,3,4,7,8-PeCDF
  and arsenic by adult subsistence farmers in subarea
  El).  The analyses of these two cases are assumed to
  be representative of the overall uncertainty associated
  with the HHRA, and may serve as a  basis for
  reasonable approximations of the  uncertainty
  associated with the overall risk estimates.
In accordance with EPA guidance (U.S. EPA 1995a), a
detailed quantitative uncertainty analysis is not performed  for
the entire HHRA; i.e., the uncertainty in the risk estimates for
exposure to every chemical to every population subgroup
through every exposure pathway at every location is not
quantitatively assessed.  As discussed in Chapter VIII, indirect
exposure to 2,3,4,7,8-PeCDF represents approximately 32%
of the total risk to subsistence farmers.   Total dioxins and
furans represent approximately 67% of the total risk.   Based
on these results,  2,3,4,7,8-PeCDF can be expected to be a
reasonable indicator of the uncertainty in the total risk
estimate.
    low
  unknown
  For the specific cases evaluated in the uncertainty
  analysis,  a variance propagation is performed using a
  limited subset of the input parameters (i.e., the
  "primary" influential parameters).  The input
  parameters not selected in the sensitivity analysis
  were assumed to have a small impact on the results
  of the variance propagation.
The "primary" influential parameters are selected based on the
results of a sensitivity analysis.  This assumption is validated
by repeating the variance propagation including an addition set
of "secondary"  influential parameters. The inclusion of the
secondary input parameters does not change the output
distributions by more than approximately 7%.  Therefore, the
exclusion from  the variance propagation of all the input
parameters that are not selected in the sensitivity analysis is
not expected to change the  output distributions by more than
10%.
    low
underestimate
Volume V
              IX-44
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                                                          TABLE IX-4 (continued)
                                                       Key Assumptions for Chapter IX
                                                            (Uncertainty Analysis)
                     Assumption
                          Basis
Magnitude
 of Effect
Direction of
   Effect
  The emissions data collected during the February
  1994 trial burn and 22 performance test runs (August
  1993 to August  1994) are assumed to represent the
  expected range of long term operating conditions and
  waste feeds from the WTI incinerator.
The performance tests were conducted using actual facility
waste feeds and a wide range of operating conditions.
Therefore, provided future waste feed compositions do not
contain substantially greater quantities of any particular
constituent, the emission rates are expected to be within the
range used in this uncertainty analysis.
   low
overestimate
  Brominated compounds are assumed not to exceed
  one third of the chlorinated aromatics in the  waste
  feed.
Based on a review of the waste profiles for WTT's first nine
months of operation, quantities of brominated compounds in
the waste feed are approximately one twentieth of the
chlorinated compounds. Therefore, this is expected to be a
conservative assumption, resulting in an overestimate of the
quantity of halogenated compounds being emitted from the
facility.
  medium
overestimate
  Lognormal distributions are assumed for most of the
  input parameters.  In particular, parameters that are
  modeled in the variance propagation by lognormal
  distributions include intake rates, emission rates,
  dispersion factor, H,  Kw, Kd,, Ba, Br, and tm.
Based on published data for most of these parameters, this is
considered to be a reasonable assumption, and has been
adopted in several other uncertainty analyses (McKone 1994;
CalEPA 1993; McKone and Ryan 1989).
   low to
  medium
  unknown
Volume  V
               IX-45
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TABLE IX-4 (continued)
Key Assumptions for Chapter IX
(Uncertainty Analysis)
Assumption
Triangular distributions are assumed for input
parameters with uncertain values and little
measurement data. In particular, parameters that are
modeled in the variance propagation by triangular
distributions include farm animal diets, , BCF, and
the wet deposition factor. Uniform distributions are
assumed for input parameters for which a range is
known and either no "most likely" value is known or
the data are evenly distributed across the range. Fn
particular, parameters that are modeled in the
variance propagation by uniform distributions include
fat fractions in beef and milk.
For parameters assumed to follow lognormal
distributions, the estimated or measured range of
values for each parameter represents the 95 percent
confidence interval.
Basis
The use of triangular and uniform distributions are expected to
be conservative assumptions.
Professional judgment is used to select conservative estimates
for the upper and lower bounds that correspond to at least a
95 percent confidence interval.
Magnitude
of Effect
low to
medium
low to
medium
Direction of
Effect
overestimate
overestimate
Notes:
low = less than a factor of two
medium = a factor of two to ten
high = greater than a factor of ten
Volume V
IX-46
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                    X. SUMMARY AND CONCLUSIONS
      This volume of the WTI Risk Assessment presents a site-specific, multipathway
assessment of human risks posed by emissions from the WTI facility.  The primary processes
that generate chemical emissions at the facility include:

      •     The incineration process, where hazardous waste is combusted in a rotary kiln
             incinerator, and chemical constituents generated during combustion are
             released along with the flue gases from the incinerator stack; and

      •     The waste feed handling and storage process, where some of the volatile
             constituents present in the waste feed may be released into the atmosphere in
             the form of fugitive emissions.

      As discussed in Volume IE, emissions from the incinerator stack are estimated
primarily by conducting stack measurements. Dioxins and furans are identified as the
constituents of primary concern in stack emissions. Fugitive emission rates of volatile
constituents in the waste feed are estimated using conservative assumptions and models that
likely overstate emissions, and are based on the  waste feed composition, as determined from
an analysis of wastes received during WTI's first year of operation.
      As discussed in Volume IV, the ISC-COMPDEP model is used to simulate the
atmospheric transport of facility emissions, and to predict vapor concentrations and particle
deposition in the vicinity of the site.  The ISC-COMPDEP model was modified to
incorporate local meteorological conditions that are influenced by the complex terrain in
which the site is  located.  Chapter VI of this volume discusses the appropriate fate and
transport models that are used to estimate concentrations in environmental media to which
individuals in the site vicinity may be exposed.  These media include air, soil, water, and
food products such as vegetables and meat.
      A study area for the risk assessment is defined to extend over a 12 kilometer (km)
radius from the facility, which encompasses the  area most affected by stack emissions. The
study area is divided  into  12 subareas,  three subareas in each north, south, east and west
direction.  The boundaries of the subareas are defined by concentric rings surrounding the
facility at radii of 3 km, 7 km, and 12 km.
Volume V                                v.i
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       Subgroups of the populations in the site vicinity are identified to adequately reflect
exposures to the entire population within the study area.  The population subgroups include
adult and child residents and farmers, as well as subgroups such as subsistence farmers and
school children that may be susceptible to higher exposures as a result of their particular
activity patterns.
       Risk to the identified subgroups are estimated by evaluating the potential for cancer
risks and noncancer effects from exposure to facility-related chemicals.  Population risks are
also evaluated based on estimates of the number of individuals in each subgroup, taking into
consideration the differing levels of exposure of the  individual subgroups based on their
particular activity patterns and locations with respect to the site.
       The uncertainty associated with individual steps of the risk assessment process are
combined in a Monte Carlo analysis, to provide estimates of the likely range of cancer risks
for the most highly exposed subgroup, the subsistence fanner, and the probability of
individual subsistence farmers experiencing risks at different  levels within this risk range.
       The following is a summary of the Human Health Risk Assessment results.

Stack Emissions

       •      Dioxins and furans are identified as the primary constituents of concern in
              stack emissions, based on the levels of measured emissions,  the likely extent
              of accumulation in food,  and the toxicity  of this class of chemicals.

       •      The expected  dioxin and furan emissions from  the facility expressed as toxicity
              equivalents is estimated to be 1.3 x  10~9 g/s.

       •      Use of the air dispersion  model, the ISC-COMPDEP model, is considered a
              reasonable means  of predicting the off-site impacts of facility emissions with
              modifications made to the model to allow incorporation of meteorological data
              collected at multiple heights at the WTI facility and at another location within
              the Ohio River Valley approximately 10 miles  away.

       •      Particle emissions consist of fine particles less  than 10 micrometers (/xm) in
              diameter, with 70 percent of the particles less than 1 /*m in diameter.  These
              emissions are not  predicted to result in exceedances of the National Ambient
              Air Quality Standards (NAAQS).
Volume V                                 v *»
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              The air dispersion model predicts the highest impacts to occur within one
              kilometer of the facility, primarily in the east-west direction.  Particle
              deposition as a result of precipitation scavenging (wet deposition) is predicted
              to be the principal deposition mechanism.

              The consumption of meat (beef, pork, and poultry) and eggs from locally
              raised livestock, and consumption of milk and dairy products (cheese, milk
              desserts,  yogurt, cream, and butter) from locally raised cows are determined to
              be the principal pathways of exposure to WTI stack-related chemicals.  In
              addition,  consumption of mother's milk is a significant pathway of exposure
              for breast-feeding infants.

              The subsistence farmer and child are identified as the subgroups with the
              highest estimated risks.
Cancer Risks
              The estimated average total cancer risk (direct and indirect) for each of the
              population subgroups is less than 1 x 10~5, or 1 in 100,000. The highest
              subarea cancer risk of 1  x 10"6 is estimated in subarea El  (the nearest subarea
              to the east of the site) for the  subsistence farmer. The estimated average
              cancer risk for the subsistence farmer child in subarea El is also
              1 x 10-6.

              The cancer risks for the adult  and child farmer are estimated to be
              approximately 2 to 3-fold lower than the subsistence farmer adult and child.
              The cancer risks for the adult  and child resident are estimated  to be
              approximately 10-fold and 3-fold lower than the subsistence farmer adult and
              child,  respectively.

              The compound 2,3,4,7,8-PeCDF (a chlorinated furan) is identified as the
              chemical primarily contributing to the estimated cancer risk for the indirect
              pathways, with the exception of breast milk ingestion.  Approximately 38
              percent of the risk to the subsistence farmer is accounted for by 2,3,4,7,8-
              PeCDF.  Dioxins and furans account for approximately  76 percent of the
              estimated risk to the subsistence fanner.
Volume V
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        •     High-end (approximately 90 percentile) exposure for the subsistence farmer is
              estimated to provide a measure of the possible variation in behavioral
              characteristics (e.g., inhalation rates) of individuals in this subgroup. The
              high-end cancer risk to the subsistence farmer is 7 x 10"6 for this subgroup in
              subarea El,  more than five times higher than the average risk.

        •     To provide an estimate of the variability in exposures within a subarea due to
              differences in exposure concentrations with location within the subarea. an
              evaluation of the risk at the point of maximum impact within each subarea is
              estimated. In general, this risk is approximately three to four times higher
              than the average risk, i.e., a cancer risk of 4 x 10^ is estimated for the
              subsistence fanner in subarea El. The likelihood, however, of a subsistence
              farmer being located at the point of maximum impact is extremely small.  The
              risks at the point of maximum impact, therefore, are hypothetical and
              presented for illustrative purposes only.

       •     An uncertainty analysis is performed for 2,3,4,7,8-PeCDF, which is the most
              significant contributor to the estimated cancer risk for the subsistence farmer
              subgroup at the point of maximum impact in  subarea El.  Based on the results
              of this uncertainty analysis, there is an approximately 95 percent likelihood
              that the cancer risk estimate for indirect exposures to 2,3,4,7,8-PeCDF for a
              subsistence fanner in subarea El  is below 3 x 10"5. This value is about 15-
              fold higher than the point estimate of 2 x 10^ for the subsistence farmer.
              Accordingly, based on available information and data regarding the key input
              parameters, there is only a small probability that cancer risks due to exposure
              to 2,3,4,7,8-PeCDF through indirect exposure pathways for subsistence
              fanners in subarea El are greater than 3 x  10~5.
Noncancer Effects
       •     The estimated average noncancer hazard indices (His) are below 1.0 for all
             population subgroups.  The total average noncancer HI values (direct plus
             indirect) estimated in subarea El for the subsistence farmer and the subsistence
             fanner child are 0.02 and 0.07, respectively.

       •     Similar to the cancer risk estimates, the noncancer HI values for the adult and
             child farmer are estimated to be lower than the subsistence farmer adult and
Volume V
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               child, approximately 1 to 2-fold. The noncancer HI values for the adult and
               child resident are estimated to be also approximately 1 to 2-fold lower than the
               subsistence fanner adult and child.

               Hexachlorophene is estimated as the chemical primarily contributing to the
               estimated noncancer HI value.  Approximately 45 percent of the estimated
               noncancer HI value for the subsistence fanner child is accounted for by this
               compound. Of the total estimated hexachlorophene HI value, meat and dairy
               ingestion account for almost the entire value (50 percent  each).

               The estimated high-end HI value for the subsistence fanner child in subarea  El
               is approximately one to two times the average HI value (i.e., the estimated
               high-end HI value for the child is 0.1 in subarea El).
 Other Subgroups
              The estimated average cancer risks for breast feeding infants of subsistence
              farmers in subarea El is 2 x 10"*.  The non-dioxin organic chemicals
              contribute approximately 66 percent of the total estimated risk with
              benzo(a)pyrene accounting for 37 percent of the total risk.  Dioxins and furans
              account for approximately 34 percent of the total estimated risk.

              Extremely low cancer risks and noncancer HI values are estimated for
              subsistence fishermen fishing in the Ohio River and Little Beaver  Creek,
              which is located in subarea N2.  The maximum risk and HI value are
              estimated to be less than 6 x 10~8 and less than 4 x 10"3, respectively. A
              noncancer HI value of 0.004 is estimated for the subsistence fisherman fishing
              Tomlinson Run Lake located in subarea S3.
Other Pollutants
              The predicted concentrations of priority pollutants such as sulfur dioxide,
              nitrogen oxides, hydrogen chloride, particles and lead are substantially below
              the National Ambient Air Quality Standards (NAAQS).
Volume V
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Fugitive Emissions
              The average cancer risks from inhalation exposure to organic vapor fugitive
              emissions for residents within a radius of 2,000 feet from the site is estimated
              to be in the range of 5 x 10"7 to 2 x 10"6. These cancer risk estimates are
              based on very conservative (overstates actual) estimates of emissions from the
              identified sources of fugitive emissions, particularly the wastewater tank and
              leakages within from the organic waste feed tank building.

              The estimated noncancer HI values are similarly overstated and range between
              0.01 and 0.07.

              Average inhalation cancer risks associated with fugitive ash emissions are
              estimated to be below 5 x 10"8.  HI values do not exceed 7 x
              Average indirect cancer risks associated with fugitive ash emissions are
              estimated to be below 4 x 10~n.  HI values for indirect exposure do not exceed
              5 x 10^.
Volume V
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-------
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-------
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Volume V                               XT-7
-------
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Volume V
-------
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-------
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                                                             /••
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Volume V                              XI-11
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Volume V                              vr.io
-------
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Volume V
-------
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    *
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                          APPENDIX V-1



                       Summary of Log K,^ Values
Volume V
-------
Summary of Log K^, Values
Substance
Log K^.
Source
PICs and Residual Organic Compounds
Acenaphthene
Acenaphthylene
Acetaldehvde
Acetone
Acetophenone
Acrolein
Acrvlonitrile
Anthracene
Benzaldehyde
Benzene
Benzoic acid
Benzotrichloride
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Benzo(e)pyrene
Benzo(g , h , i)pery lene
Benzo(j)fluoranthene
Benzo(k)fluoranthene
Benzyl chloride
Biphenyl
Bis(2-chloroethoxy)methane
Bis(2-chloroethyl)ether
Bis(2-chiaroisopropyl)ether
Bis(2-ethylhexyl)phthalate
Bromochloromethane
Bromodichloromethane
Bromoethene
Bromoform
Bromomethane
Bromodiphenyl ether, p-
Butadiene. 1,3-
Butanone, 2- (MEK)
Butylbenzylphthalate
Carbon disulfide
3.92
4.07
0.43
-0.24
1.64
-
0.25
4.55
-
2.13
1.86
2.92
5.70
6.11
6.20
-
6.70
-
6.20
-
-
1.26
1.21
2.58
7.30
-
2.10
-
2.35
1.19
5.00
-
0.28
4.84
2.00
a
b
b
a
a
c
a
a
c
a
a
b
a
a
a
c
a
c
a
c
c
b
a
a
a
c
a
c
a
a
a
c
**•'
a
a
a
Volume V
Appendix V-l
-------
Summary of Log Km Values
Substance
Carbon tetrachloride
Chlordane
Chloro-3-methylphenol. 4-
Chloroacetophenone, 2-
Chloroaniline, p-
Chlorobenzene
Chlorobenzilate
Chloroethane
Chloroform
Chloromethane
Chloronaphthalene. beta
Chlorophenol, 2-
Chlorodiphenyl ether, 4-
Chloropropane, 2-
Chrysene
Cresol. m-
Cresol, o-
Cresol, p-
Crotonaldehyde
Cumene
D, 2,4-
DDE, 4,4'-
Dibenz(a, h)anthracene
Dibenz(a,h)fluoranthene
Dibromo-3-chloropropane, 1,2-
Dibromochloromethane
Dichloro-2-butene, cis-1,4-
Dichloro-2-butene, trans-1,4-
Dichlorobenzene, 1,2-
Dichlorobenzene, 1,3-
Dichlorobenzene, 1,4-
DicbJorobenzidine, 3,3'-
Dichlorobiphenvl
Dichlorodifluoromethane
Dichloroethane, 1,1-
Dichloroethane, 1,2-
LogK»
2.73
6.32
3.10
-
1.85
2.86
4.38
1.54
1.92
0.91
4.12
2.15
4.95
-
5.70
1.97
1.99
1.95
0.63
3.58
2.70
6.76
6.69
d
-
2.24
-
-
3.43
3.72
3.42
3.51
5.58
2.16
1.79
1.47
Source
a
a
b
c
a
a
a
b
a
a
b
a
a
c
a
a
a
a
b
a
a
a
a
d
c
b
c
c
a
b
a
a
b
a
a
a
Volume V
Appendix V-l
-------
Summary of Log K^, Values
Substance
Dichloroethene, 1,1-
Dichloroethene. trans-1.2-
Dichlorofluoromethane
Dichlorophenol, 2,4-
Dichloropropane, 1,2-
Dichloropropene', cis-1,3-
Dichloropropenee, trans-1,3-
Diethylphthalate
Dimethoxybenzidine, 3,3'-
Dimethylphenol, 2,4-
Dimethylphthalate
Di-n-butylphthalate
Dinitrotoluene, 2,6-
Dinitro-2-methylphenol, 4,6-
Dinitrobenzene, 1,2-
Dinitrobenzene, 1,3-
Dinitrobenzene, 1,4-
Dinitrophenol, 2,4-
Dinitrotoluene, 2,4-
Dioxane, 1,4-
Di(n)octylphthalate
Ethyl methacrylate
Ethyl benzene
Ethylene dibromide
Ethylene oxide
Ethylene thiourea
Fluoranthene
Fluorene
Formaldehyde
Furfural
Heptachlor
Heptachlorobiphenyl
Hexachlorobenzene
Hexachlorobiphenyl
Hexachlorobutadiene
Hexachlorocyclohexane. alpha-
LogK^
2.13
2.07
-
3.08
1.97
2.00
2.00
2.50
1.81
2.36
1.57
4.61
1.87
2.85
-
-
-
1.55
2.01
-0.39
8.06
1.59
3.14
1.75
-0.22
-0.66
5.12
4.21
-0.05
0.41
6.26
7.70
5.89
7.17
4.81
-
Source
a
a
-
a
a
a
a
a
a
a
a
a
a
b
c
c
c
a
a
a
a
a
a
a
b
a
a
a
a
b
a
f
a
f
a
c
Volume V
Appendix V-l
-------
Summary of Log KO, Values
Substance
Hexachlorocyclobexane, beta-
Hexachlorocyclobexane, gamma-
CLindane)
Hexachlorocyclopentadi ene
Hexachloroethane
Hexachlorophene
Hexane. n-
Hexanone. 2-
Hexanone, 3-
Indeno(l ,2,3-cd)pyrene
Isophorone
Maleic hydrazide
Methoxychlor
Methyl-tert-butyl ether
Methyl-2-pentanone, 4- (MIBK)
Methylene bromide
Methylene chJoride
Metbylnaphthalene, 2-
Monochlorobiphenyl
Naphthalene
Nitroaniline, 2-
Nitroaniline, 3-
Nitroaniline, 4-
Nitrobenzene
Nitrophenol, 2-
Nitrophenol, 4-
N-Nitroso-di-n-butylamine
N-Nitroso-di-n-propylamine
N-Nitrosodiphenylamine
Nonachlorobiphenyl
Octachlorobiphenyl
Pentachlorobenzene
PentachJorobiphenyl
Pen tachl oroni trobenzen e
Pentachlorophenol
Phenanthrene
LogK,,.
-
3.73
5.39
4.00
7.54
-
1.38
-
6.65
1.70
-0.32
5.08
1.24
1.19
-
1.25
4.11
6.04
3.36
1.85
1.37
1.39
1.84
1.79
2.04
2.41
1.40
3.16
6.04
6.04
5.26
7.12
4.64
5.09
4.55
Source
c
a
a
a
a
c
b
c
a
a
b
a
b
a
c
a
b
b
a
b
b
b
a
b
b
a
a
a
b
b
a
f
*•
a
a
a
Volume V
Aooendix V-1
-------
Summary of Log Iv, Values
Substance
Phenol
Phosgene
Propionaldehvde
Pvrene
Quinoline
Quinone
Safrole
Stvrene
Tetrachlorobenzene, 1,2.4,5-
Tetrachlorobiphenyl
Tetrachloroethane, 1,1,1,2-
Tetrachloroethane, 1,1,2,2-
Tetrachloroethene
Tetrachlorophenol, 2,3.4,6-
Toluene
Toluidine, o-
Toluidine, p-
Trichloro-l,2.2-TFE, 1,1,2-
Trichlorobenzene, 1.2,4-
Trichlorobiphenyl
TrichJoroethane, 1,1,1-
Trichloroethane, 1,1,2-
Trichloroethene
Trichlorofluoromethane
Trichlorophenol, 2,4,5-
Trichlorophenol, 2,4,6-
Trichloropropane, 1,2,3-
Vinyl acetate
Vinyl chloride
Xylene, m-
Xylene, o-
Xylene, p-
LogK,.
1.48
-
-
5.11
-
-
2.66
2.94
-
6.21
2.63
2.39
2.67
4.10
2.75
-
-
3.16
4.01
5.58
2.48
2.05
2.71
2.53
3.90
3.70
-
0.73
1.50
3.20
3.13
3.17
Source
a
^
c
a
c
c
a
a
c
f
a
a
a
b
a
c
c
a
a
b
a
a
a
a
a
a
c
a
a
a
a
a
Dioxin and Furan Congeners
2,3,7,8-TCDD
1,2,3,7,8-PeCDD
1.2,3,4,7,8-HxCDD
6.64
6.64
7.79
f
f
f
Volume V
Appendix V-l
-------
                                       Summary of Log K^ Values
                  Substance
                             Source
   1.2.3,6,7,8-HxCDD
7.30
   1,2.3,7.8.9-HxCDD
7.79
   1,2,3.4.6.7,8-HpCDD
8.20
   OCDD
7.59
   2,3.7,8-TCDF
6.53
   1.2,3.",8-PeCDF
6.79
   2.3,4,7.8-PeCDF
6.92
   1,2,3,4.7,8-HxCDF
7.30
   1,2,3,6,7,8-HxCDF
7.30
   2.3,4,6.7,8-HxCDF
7.30
   1.2.3.7.8.9-HxCDF
7.30
   1.2,3.4.6,7.8-HpCDF
7.90
   1,2.3,4,7,8,9-HpCDF
7.90
   OCDF
8.80
   Notes
   a -      Recommended value in U.S. EPA 1995.
   b -      Maximum value from Howard 1993, Hazardous Substance Dau Bant (HSDB), Montgomery and Welkom 1990. U.S. EPA
           1990, and Verschueren 1983
   c -      Log Km value not needed because an emission rate could not be estimated for this chemical.
   d -      A value could not be found for this chemical.
   e -      The isomer was not specified, so the value is assumed to apply to both forms
   f-      U.S. EPA 1994
   MEK -   methyl ethyl ketone
   MIBK -   methyl isoburyl ketone
   TFE -    trifluoroethane
Volume V
AnnenHiv V-1
-------
                                   REFERENCES
 Howard, P.H. (Ed.) 1993. Handbook of Environmental Fate and Exposure Data for Organic
        Chemicals.  Lewis Publishers. Chelsea, Michigan.

 Montgomery, J.H., and L.M.  Welkom.  1990.  Groundwater chemicals desk reference. Le\\ is
        Publishers.  Chelsea, Michigan.

 U.S. Environmental Protection Agency (U.S. EPA).  1990.  Basics of pump-and-trea: ground-
        water remediation technology. Robert S. Kerr Environmental Research laboratory. Ada.
        OK.  EPA/600/8-90/003.  March.

 U.S. Environmental Protection Agency (U.S. EPA).  1994.  Estimating exposure to dioxin-like
        compounds,  Vol III: Site-Specific Assessment Procedures.  Review Draft.  Office  of
        Research  and Development, Washington, D.C. EPA/600/6-88-005Cc.

 U.S. Environmental Protection Agency (U.S. EPA).  1995.  Internal report on summary  of
       measured, calculated and recommended  log  Km. values.  Environmental Research
       Laboratory-Athens.  April 10.

 Verschueren, K.  1983. Handbook of Environmental Data on Organic Chemicals, 2nd edition.
       Van Nostrand Reinhold Co.  New York.
Volume V
-------
This page intentionally left blank.
-------
                              APPENDIX V-2

              Physical/Chemical Parameter Values and Toxicity Values
                 Used in Selection of Surrogate Organic Chemicals
                               (Stack Emissions)
Volume V
-------
 Table 1 Results of i
Chemical Surrogate Selection
  CHEMICAL

  Acenaphlhenc
  Acenaphlhylene
  Acelaldehyde
  Acetone
  Acetophenone
  Acrylonitrile
  Anthracene
  Benzene
  Benzole acid
  Benzotrichloride
  Benzo(a (anthracene
  Benzofajpyrene
  Benzojbjfluoranthene
  Benzo(g,h,i)perylene
  Benzo(k)(luoranthene
  Bis(2-chloroethoxy) methane
  Bis(2-chloroethyl)elher
  Bis(2-chlofoisopropyl)ether
  Bls(2-«thylh«)(yl)phtbalale
  Bromodichloromethane
  Bromo(onn
  Btomomelhane
  Bromophenyl phenylether
  Butanone, 2- (Methyl ethyl ketone)
  Butylbenzylphthalate
  Carbon disulfide
  Carbon tetrachlorlde
  Chlordane
 Chforo-3-methylphenol, 4-
 Chloroaniline, p- (4-Chloroaniline)
 Chlorobenzene
 Chlorobenzilate
 Chloroethane (Ethyl chjoride)
 Chloroform
 Chloromethane
 Chloronaphthalene, 2-
 Chlorophenol, 2-
 Chloropheriyl-phenyl ether, 4-
 Chrysene
 Cresol, m-
 Cresol, o- (2-Methylphenol)
 Cresol, p-
 Crotonaldehyde
 Cumene
 DDE, 4.4'-
CAS
Number
83329
208 968
75-07 0
67-64 1
98-86 2
107-13-1
120-12-7
71-43-2
65-85-0
98-07-7
56-55-3
50-32-8
205-99-2
191-24-2
207-08-9
111 91-1
111-44-4
108-60 1
117-81-7
75-27-4
75-25 2
74-83-9
101-55-3
78-93-3
85 68-7
75-150
S6-23-5
57-74-9
59-50-7
106-47-8
108-90-7
510-15-6
75-00-3
67-66-3
74-87-3
91-58-7
95-57-8
7005-72-3
218-01-9
108-39-4
95-48-7
106-44-5
4170-30-3
98828
72-559
Average
Emission
Rale (g/s)
669E 06
669E-06
3-01E-04
290E-03
293E-04
2 02E-04
550E-06
1 47E-05
1 13E-05
3 20E-05
5 50E-06
5.50E-06
5.50E-08
550E06
5 50E-06
669E-06
1 33E 05
669E-06
3.72E-05
1 03E-04
550E-06
4 90E 04
6 69E 06
5 14E-05
550E-06
891E-05
1.58E-04
5 50E-07°
6 69E-06
6 69E-06
5 50E-06
3 68E-05
4 90E-04
2 66E-04
2 45E-04
6 69E-06
5 50E-06
6 69E-06
550E-06
550E-06
550E-06
550E-06
1 39E-04
550E-06
5 50E-07
High end
Emission
Rate (g/s)
669E-06
669E 06
301E04
290E03
293E-04
202E-04
1 10E-05
2 63E-05
1 13E-05
3 20E-05
1 10E 05
1.10E-05
1.10E45
1 10E-05
1 10E 05
6 69E 06
1 33E-05
6 69E-06
5.23E45
1 53E 04
1 10E-05
9 80E-04
6 69E-06
740E-05
1 IDE 05
9 46E-05
2.75E-04
1 10E-06
6 69E-06
6 69E-06
1 10E-05
3 68E-05
9 80E-04
4 07E-04
4 90E-04
6 69E-06
1 10E-05
6 69E-06
1 10E 05
1 IDE 05
1 10E-05
1 10E-05
1 39E-04
1 10E 05
1 10E-06
source
MRI estimate
MRI
MRI
MRI
MRI
estimate
estimate
estimate
estimate
MRI estimate
8/94 PIC test
8/94 PIC lesl
MRI estimate
MRI
8/94
8/94
8/94
8/94
MRI
estimate
PIC test
PIC lest
PIC test
PIC test
PIC (est
estimate
MRI estimate
MRI
8/94
8/94
8/94
8/94
MRI
8/94
8/94
8/94
8/94
8/94
MRI
MRI
8/94
estimate
PIC lesl
PIC lesl
PIC lesl
PIC lesl
estimate
PIC test
PIC test
PIC test
PIC test
PIC test
estimate
estimate
PIC test
MRI estimate
8/94
8/94
8/94
MRI
8/94
MRI
8/94
8/94
8/94
8/94
PIC test
PIC test
PIC test
estimate
PIC test
estimate
PIC lest
PIC lest
PIC test
PIC test
MRI estimate
8/94
8/94
PIC test
PIC test




SF
NA
NA
NA
NA
NA
5 40E-01
NA
2 90E-02
NA
1
7
7.
7
7

1

1
30E+01
30E-01
30E+00
NA
30E-02
NA
10E4OO
NA
.40E42
6 20E-02
7 90E-03





1
1



2

8
1



7



NA
NA
NA
NA
NA
30E-01
30E+OO
NA
NA
NA
70E-01
NA
1 0E-02
30E-02
NA
NA
NA
30E03
NA
NA
NA
1 90E+00

3
NA
40E-01
RfD
60E02
6 OE-02
2 6E-03
1 OE 01
1 OE-01
5 7E 04
3 OE-01
NA
40E+00
NA
NA
NA
NA
NA
NA
NA
NA
4 OE-02
2 OE-02
2 OE-02
2 OE-02
1 4E-03
NA
2 9E-01
2 OE-01
29E-03
7.0E-04
60E-05
NF
4 OE-03
5 7E-03
2 OE-02
29E400
1 OE-02
NA
8 OE-02
5 OE-03
NF
NA
50E02
50E 02
5 OE-03
NA
26E-03
NA
Kow
832E+03
1 17E+04
269E+00
5 75E-01
437E+01
1 78E+00
355E+04
1 35E+02
724E+01
832E+02
5 01 E +05
1.29E+06
1.58E+06
501E406
1 58E+06
1.82E+01
1 62E+01
3 80E+02
2.00E+07
1 26E+02
2 24E+02
1 55E+01
100E+05
191E+00
6 92E+04
1 OOE+02
5.37E+02
209E*06
1 26E+03
7 08E+01
724E+02
2 40E+O4
347E+01
8 32E+01
8 13E+00
1 32E+04
1 41E+02
891E+04
501E*05
933E+01
977E»01
891E«01
427E+00
380E*03
575F40G
Average
QCB
Score
NoSF
NoSF
NoSF
No SF
NoSF
1 94E-04
NoSF
5 76E-05
NoSF
3 46E-01
201E+00
5.17E+01
6.36E+00
NoSF
6 36E-01
NoSF
2 37E-04
NoSF
1.04E+01
8 05E-04
9 73E-06
NoSF
NoSF
NoSF
NoSF
NoSF
1.11E-02
1 49E+00
NoSF
NoSF
NoSF
2 38E-01
NoSF
1 79E-03
2 59E-05
NoSF
NoSF
NoSF
201E-02
NoSF
NoSF
NoSF
1 1 3E 03
NoSF
1 OBF'OO
Average Chemical Retained?
QNB Cancer Non-cancer
Score Effects Effects
9 27E-01
1 31E+00
3 15E-01
1 67E-02
1 2BE-01
6 29E-01
6 50E 01
No RfD
2 05E-04
No RfD
No RfD
No RID C
No RID C
No RfD
No RfD
No RID
No RID
6 36E-02
3.71E+04 C NC
6 49E-01
6 16E-02
5.42E+00
No RfD
3 43E-04
1 90E+00
312E+00
1.21E+02 NC
1 92E+04
No RfD
1 18E-01
697E 01
441E+01
5 95E-03
221E+00
No RID
1 10E+00
1 55E 01
No RID
No RfD
1 03E 02
1 07E 02
9 80E 0?
No RfU
B 13E'(K)
NoRIf)
'olume V, Appendix V-2
-------
able 1 Results ol Slack Chemical Sunogale Selection
CHEMICAL

Dlbenz(a,h)anthracene
Dibromochloromelhane
Dichlorobenzene, 1,2-
Dichlorobenzene, 1.3-
Dichlorobenzene, 1.4-
Dichlorobenzidine, 3,3'-
Dichlorodifluoromethane
Dichloroethane, 1,1- (Elhylidene dichloride)
Dichloroelhane, 1,2-
Dichloroethene, 1,1- (Vinylidinc chloride)
Dichloroethylene (trans), 1,2-
Dichlorophenol, 2,4-
Dichtoropropane, 1,2- (Propylene dichloride)
Dichloropropene (cis), 1,3-
Dichloropropene (Irans), 1.3-
Dielhylphthalate
Dimethoxybenzidine,  3,3'-
Dimelhylphenol, 2,4-
Dimethylphlhalate
Di-n-Butytphthalale
OinHrHoluene, 2,6-
Dinitro-2-melhylphenol, 4,6-
OinilrophenoJ, 2,4-
Dinitrotoluene, 2,4-
Oioxane, 1,4-
Ol(n|octyl phthalate
3,2.4-
Ethyl methacrylate
Ethylbenzene
Elhylene dibromide
Ethylene oxide
Ethylene thiourea
:luoranthene
:luorene              "•;
:ormaldehyde
:urfural
ieptachlor
lexachlorobenzene
lexachlorobutadlene
lexachlorocyclohexane, g- (Lindane)
texachlorocyclopentadlene
lexachloroethane
lexachlorophene
(exanone, 2-
ideno(1,2,3-cd|pyrene

CAS
Number
53-703
124-48-1
95-50-1
541-73-1
106-46-7
91-94-1
75-71-8
75-34-3
107-06-2
75-35-4
156-60-5
120-83-2
78-87-5
542-75-6
10061-026
8466-2
119-90-4
10567-9
131-11-3
84742
606-202
534-52-1
51-28-5
121-14-2
123-91-1
117-84-0
94-75-7
97-63-2
100-41-4
106-93-4
75-21-8
96-45-7
206-44-0
86-73-7
50-00-0
98-01-1
76-44-8
118-74-1
8748-3
58-89-9
77-47-4
67-72-1
70-30-4
591-78-6
193-39-5
Average
Emission
Rate (g/s)
5.50E-06
263E-05
550E-06
550E-06
550E-06
3 33E-05
2 45E-04
25E-05
25E-05
25E-05
25E-05
550E-06
25E-05
25E-05
25E05
1 69E-05
1 15E-04
550E-06
550E-06
1 57E-05
550E-06
5 50E-06
5 50E-06
550E-06
4 94 E 04
5.50E-08
3 88E-05
2 45E-04
4 98E-04
1 15E-04
305E-05
1 46E-10
550E-06
6 69E-06
6 07E-04
550E-06
5.50E-07
5.50E-06
1.01E-04
5 48E 05
S.50E-06
550E-06
3.20E45
6 43E-05
5.50E46
High end
Emission
Rale (g/s)
1.10E45
2 63E 05
1 IDE -05
1 IDE -05
1 10E-05
3 33E-05
4 90E-04
2 50E-05
2 50E-05
2 50E-05
250E-05
1 10E-05
250E-05
250E-05
2 50E-05
3 60E-05
1 15E-04
1 10E-05
1 10E-05
2 04E-05
1 10E-05
1 10E-05
1 10E-05
1 10E-05
4 94E-04
1.10E-05
3 88E-05
4 90E-04
7 53E-04
1 15E-04
3 05E-05
1 46E-10
1 10E-05
6 69E-06
6 07E-04
1 10E-05
1.10E-08
1.10E-05
1.01E-04
5 48E-05
1.10E-05
1 10E-05
320E-05
643E05
1.10E-05


source
8/94 PIC test
MR I estimate
8/94 PIC lest
8/94 PIC test
8/94 PIC test
MRI estimate
8/94 PIC test
8/94 PIC test
8/94 PIC lest
8/94 PIC test
8/94 PIC lest
8/94 PIC test
8/94 PIC lest
8/94 PIC lest
8/94 PIC test
8/94 PIC test
MRI estimate
8/94 PIC lest
8/94 PIC test
8/94 PIC lest
8/94 PIC lesl
8/94 PIC lest
8/94 PIC test
8/94 PIC lesl
MRI estimate
8/94 PIC lesl
MRI estimate
8/94 PIC lesl
8/94 PIC test
MRI estimate
MRI estimate
MRI estimate
8/94 PIC test
MRI estimate
MRI estimate
8/94 PIC test
8/94 PIC lest
8/94 PIC lesl
MRI estimate
MRI estimate
8/94 PIC test
8/94 PIC test
MRI estimate
MRI estimate
8/94 PIC test

SF

7.30E+00
8 40E-02
NA
NA
2 40E-02
4 50E 01
NA
NA
9 10E-02
1 20E+00
NA
NA
6 80E-02
1 80E-01
1 80E-01
NA
1 40E-02
NA
NA
NA
6 BOE-01
NA
NA
6 80E-01
1 10E-02
NA
NA
NA
NA
8 50E+01
1 02E+00
1 10E-01
NA
NA
4 50E-02
NA
4.50E+00
160E+00
7.80E42
1 30E+00
NA
1 40E 02
NA
NA
7.30E41

RfD

NA
20E-02
5 7E-02
NA
23E-01
NA
5 7E-02
1 OE-01
NA
90E-03
2 OE-02
3 OE-03
1 1E-03
3 OE-04
3 OE-04
8.0E-01
NA
20E-02
NA
1 OE-01
1 OE-03
NF
2 OE-03
2 OE-03
NA
2.0E-02
1 OE-02
9 OE-02
1 OE-01
57E-05
NA
80E-05
4 OE-02
4 OE-02
2 OE-01
3 OE-03
5.0E-04
8.0E-04
2.0E-04
30E04
2.0E-05
1 OE 03
3.0E-04
NF
NA

Kow

490E+06
1 74E+02
269E+03
525E+03
263E+03
324E+03
1 45E+02
617E+01
295E+01
35E+02
17E+02
20E+03
9 33E401
OOE+02
OOE+02
3 16E+02
6 46E+01
2 29E+02
3 72E+01
407E+04
7.41E+Q1
708E+02
3 55E+01
1 02E+02
4 07E-01
1.15E+08
501E+02
3 89E+01
1 38E+03
562E+01
6 03E-01
2 19E-01
1 32E+05
1 62E+04
891E-01
2 57E+00
1.82E+08
7.76E+05
646E+04
537E+03
245E»05
1 OOE+04
3.47E*07
240E«01
4.47E«06
Average
QCB
Score
1.97E*02
3 84E-04
NoSF
NoSF
3 47E-04
4 85E-02
NoSF
NoSF
3 36E-05
2 02E-03
NoSF
NoSF
7 93E-05
2 25E4)4
225E-04
NoSF
1 04E-04
NoSF
NoSF
NoSF
2 77E-04
NoSF
NoSF
3 83E-04
221E-06
NoSF
NoSF
NoSF
NoSF
550E-01
1 87E-05
351E-12
NoSF
NoSF
2 43E-05
NoSF
4.50E+00
8.83E+00
5.09E-01
3 83E-01
NoSF
7 70E-04
NoSF
NoSF
1.79E»01
Average
QNB
Score
No RID
2 29E-01
2 59E-01
No RfD
6 33E-02
No RfD
620E-01
7.71E-03
No RfD
1 87E-01
7 34E-02
220E+00
102E+OO
417E+00
417E400
666E-03
No RfD
630E-02
No RfD
638E+00
4 08E-01
No RfD
976E-02
2.81 E-01
No RfD
3.18E+04
194E+00
1 06E-01
688E+00
1 13E+02
No RfD
3 99E-07
1 81E*01
271E+00
2 70E 03
471E03
2.00E*03
5.34E*03
326E»04
981E»02
675E«04
550E»01
3.70E«06
NoRtD
No RfD
Chemical Retained'
Cancer Non-cancer
Effects Effects
C
























NC










C
C
NC

NC

NC

C
 lume V, Appendix V-7
-------
Table 1  Results ol !
'Chemical Surrogate Selection
 CHEMICAL

 Isophorone
 Maleic hydrazide
 Methoxychlor
 Methyl t-butyl ether
 Melhyl-2-Pentanone. 4- (MIBK)
 Methylene chloride
 Methylnaphthalene, 2-
 Naphthalene
 NHroanilihe, 2-
 Nrtroaniline, 3-
 Nitroaniline, 4-
 Nftrobenzene
 Nitrophenol, 2-
 Nilrophenol, 4-
 N-Nitroso-di-n-bufylamme
 N-Nitroso-di-n-propylamine
 N-NHrosodiphenylamine (Diphenylamine)
 Pentachtorobenzene
 Pentachloronrtrobenzene
 Pentachlorophenol
 Phenanlhrene
 Phenol
 Pyrene
 Salrole (5-(2-Propenyl)-1,3-benzodioxole)
 Slyrene
 Tetrachtoroethane, 1,1,1,2-
 i etrachtoroethane, 1,1,2,2-
 Tetrachtoroethene
 Tetrachtorophenol, 2,3,4,6-
 Toluene
 Trfchloro-1,2,2-trifluoroethane, 1,1,2-
 Trichforobenzene, 1,2,4-
 Trichloroethane, 1,1,1 v(Methyl chloroform)
 Trichloroethane, 1,1,2-'
 Trichloroethene
 Trichlorofluoromethane
 Trichlorophenol, 2,4,5-
 Trichlorophenol, 2,4,6-
 Vinyl acetate
 Vinyl chloride
 Xylene, m- (m-Dimethyl benzene)
 Xylene, o- (o-Dimethyl benzene)
 Xylene, p- (p-Dimethyl benzene)
 Monochlorobiphenyl
 Dichlorobiphenyl

CAS
Number
78-59 1
123-33 1
72435
1634-04 4
108-10-1
75-092
91-57-6
91-20-3
88-74-4
99-092
100-01-6
98-95-3
88-75-5
100-02-7
924 163
621-64 7
86-306
608-93-5
8268-8
8786-5
85-01-8
108-95-2
129-000
94-59-7
100-425
630-20-6
79-34-5
127-18-4
58-90-2
108-88-3
76-13-1
120-82-1
71-55-6
79-00-5
79-01-6
75-69-4
95-95-4
88-06-2
10805-4
75-01-4
108-38-3
9547-6
10642-3
NA
NA
Average
Emission
Rale (g/s)
669E-06
1 15E-04
550E-07
1 25E 05
1 25E 05
3 96E-04
4 18E-05
550E-06
6 69E-06
6 69E-06
6 69E-06
550E-06
6 69E-06
550E-06
1 21 E 04
6 69E-06
6 69E-06
4 76E 05
3 37E-05
550E06
669E-06
550E06
550E06
1 15E-04
2 25E 05
550E-06
550E-06
513E05
6 80E-06
613E-04
3 30E-04
550E-06
1 25E-05
1 25E-05
1 86E-05
2 45E-04
550E-06
550E06
6 43E-05
2 45E-04
380E-04
5 50E-06
380E-04
1 67E-08
4 68E-08
High end
Emission
Rate (g/s)
669E 06
1 15E 04
1 10E 06
2 50E-05
250E 05
6 19E-04
4 18E-05
1 10E-05
6 69E-06
6 69E-06
6 69E-06
1 10E-05
669E06
1 10E 05
1 21 E 04
6 69E-06
6 69E-06
4 76E 05
3 37E-05
1 10E 05
6 69E 06
1 10E 05
1 10E 05
1 15E-04
4 04E-05
1 10E-05
1 10E-05
8 02E 05
680E-06
1 03E-03
3 30E 04
1 10E-05
250E05
250E-05
3 09E-05
4 90E 04
1 10E-05
1 10E-05
6 43E 05
4 90E-04
564E-04
1 10E-05
564E-04
299E08
822E 08


source
MRI estimate
MRI estimate
8/94 PIC test
8/94 PIC lest
8/94 PIC test
8/94 PIC lest
MRI estimate
8/94 PIC test
MRI estimate
MRI estimate
MRI estimate
8/94 PIC tesl
MRI estimate
8/94 PIC test
MRI estimate
MRI estimate
MRI estimate
MRI estimate
MRI estimate
8/94 PIC test
MRI estimate
8/94 PIC test
8/94 PIC test
MRI estimate
8/94 PIC test
8/94 PIC test
8/94 PIC test
8/94 PIC test
MRI estimate
8/94 PIC test
MRI estimate
8/94 PIC test
8/94 PIC test
8/94 PIC test
8/94 PIC test
8/94 PIC test
8/94 PIC test
8/94 PIC test
MRI estimate
8/94 PIC lest
8/94 PIC test
8/94 PIC test
8/94 PIC lest
8/94 PIC test
8/94 PIC lest

SF

9 50E 04
NA
NA
NA
NA
7 50E 03
NA
NA
NA
NA
NA
NA
NA
NA
5 40E+00
700E+00
4 90E-03
NA
260E-01
1 20E-01
NA
NA
NA
NA
NA
260E-02
2.00E-01
5 20E-02
NA
NA
NA
NA
NA
5 70E-02
1 10E-02
NA
NA
1 10E-02
NA
1 90E+00
NA
NA
NA
7 70E+00
7 70E+00

RfO

20E 01
50E 01
50E-03
86E 01
NF
60E-02
NF
NA
5 7E-05
NF
NF
5 OE-04
NF
NF
NA
NA
NA
NA
30E-03
3 OE-02
NA
6 OE-01
3 OE-02
NF
2 OE-01
3 OE-02
NA
1 OE-02
3 OE-02
1 1E-01
86E+00
1 OE-02
NA
4 OE-03
NA
2 OE-01
1 OE-01
NA
5 7E-02
NA
20E+00
20E+00
NA
NA
NA

Kow

501E+01
4 79E-01
1 20E+05
1 74E+01
1 55E+01
1 78E+01
1 29E+04
2 29E+03
7 08E+01
2 34E+01
2 45E+01
692E+01
617E+01
1 10E+02
257E+02
251E+01
1 45E+03
1 82E+05
4 37E+04
1 23E+05
3 55E+04
3 02E+01
129E+05
4 57E+02
871E+02
4 27E+02
2 45E+02
4 68E+02
1 26E+04
5 62E+02
1 45E+03
1 02E+04
3 02E+02
1 12E+02
5 13E+02
3 39E+02
7 94E+03
5 01 E +03
537E+00
316E+01
1 58E+03
1 35E+03
1 48E»03
1 10E«06
380F*05
Average
QCB
Score
3 19E-07
NoSF
NoSF
NoSF
NoSF
5 28E-05
NoSF
NoSF
NoSF
NoSF
NoSF
NoSF
NoSF
NoSF
1 68E-01
1 18E-03
474E-05
NoSF
3 82E-01
8 12E-02
NoSF
NoSF
NoSF
NoSF
NoSF
610E-05
270E-04
1 25E-03
NoSF
NoSF
NoSF
NoSF
NoSF
799E-05
105E-04
NoSF
NoSF
3 03E-04
NoSF
1 47E-02
NoSF
NoSF
NoSF
1 41E 01
1 37E 01
Average
QNB
Score
1 68E-03
1 1 0E-04
1 32E+01
2 53E-04
NoRfD
1 17E-01
NoRfD
NoRfD
829E+00
NoRfD
NoRfD
761E-01
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
4 90E+02
2 26E+01
NoRfD
2 77E-04
2 36E+01
NoRfD
9 80E-02
7 82E-02
NoRfD
2 40E+00
2 BSE +00
301E+00
556E02
563E+00
NoRfD
3 51 E 01
NoRfD
4 15E 01
437E01
NoRfD
6 04E-03
NoRfD
301E 01
371E03
No RfD
Mo RID
No RIO
                                                                                                                                                             Chemical Retained'
                                                                                                                                                             Cancer  Non-cancer
                                                                                                                                                             Effects     Effects
 'olume V, Appendix V-2
-------
Table 1 Results of Slc":k Chemical Siruogate Selection
 CHEMICAL

 Trichlorobiphenyl
 Tetrachloroblphenyl
 Penlachtofobiphenyl
 Hexachloroblphenyl
 Heplachloroblphenyl
 OctacMorobiphenyl
 Nonachkxobiphenyl
 2.3,7,1-TCDD
 1,2,3.7,8 PeCDD
 1,2,3,4,7,8-HxCDD
 1,2,3,6,7,8-HxCDD
 1.2,3,7,8,9-HxCDD
 1,2,3,4,6,7,8-HpCDD
 OCDO
 2,3.7,8-TCOF
 1,2,3,7,8-PeCDF
 2,3,4,7,8-PeCDF
 1,2,3,4,7,8-HxCDF
 1,2,3,6,7.8 HxCDF
 2,3,4,8,7.8-HxCDF
 1.2,3,7 ,a,9-HxCOF
 1,2,3,4.e,7,8-HpCDF
 1,2,3,4.7,8.9-HpCDF
 OCDF

CAS
Number
NA
NA
NA
NA
NA
NA
NA
1746-014
40321-76-4
39227-28-6
57653-857
19408-74-3
35822-469
3268-87-9
51207-31 9
57117-41-8
57117-31-4
70648 26-9
57117-449
60851-34-5
72918 21 9
67562-39-4
55673497
39001424
Aveiage
Emission
Rale (g/s)
302E08
1.40E4B
1.40E-08
1.40E48
1.40E48
1 40E-08
1 40E-08
1.08E11
6.78E-11
8.95E-11
1.66E-10
109E-10
1.24E49
6.15E49
8.77E-11
3.45E 10
4.67E-10
1.43E49
1 33E49
1.50E49
293E-10
9.30E49
1.22E49
1.89F48
High end
Emission
Rate (g/s)
5 80E 08
280E-08
280E08
280E48
2.80E48
2 80E 08
2 80E 08
2.16E-11
9.46E-11
1.25E-10
2.18E-10
1.SSE-10
1.69E49
9.BOE49
1.15E-10
4.35E-10
604E-10
1.85E49
1.71E49
1.96E49
3.85E-10
1.30E48
1.80E49
3.62E48
     source

  8/94 PIC lest
  8/94 PIC lest
  8/94 PIC lest
  8/94 PIC lest
  8794 PIC test
  8/94 PIC test
  8/94 PIC test
26 post ECIS runs
26 post-ECIS runs
26 posf-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 posf-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
26 post-ECIS runs
28 post-ECIS runs
26 post-ECIS runs

SF

7 70E *00
7 70E»00
7 70E*00
7 70E+00
7.70E»00
7 70E+00
7 70E+00
1.50E+05
7.50E+04
1.50E+04
1.SOE+04
1.SOE+04
150E+03
1.50E*02
1.50E+04
7.SOE+03
7.50E+04
1.SOE+04
1.50E+04
1 50E+04
1.50E+04
1.50E+03
1.50E+03
1.50E+02


RID

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
TOTAL

Row

380E*05
162E+06
1 32E+07
1.48E*07
5.01 E»07
1 10E+06
1 IDE +06
4.37E+06
4.37E+08
6.17E+07
2.00E+07
8.17E»07
158E*08
389E+07
3.39E*06
8.17E+08
8.32E+08
2.00E+07
2.00E+07
2.00E*07
2.00E+07
7.94E*07
7.94E+07
«.31E»08
SUM =
Aveiage
QCB
Score
B 85E 02
1.75E4M
1 42E+00
1 59E+00
5.40E+00
1 18E-01
1 18E-01
7.07E+00
2.22E+01
8.28E+01
496E+01
1.01E*02
2.95E+02
359E+01
4.46E+00
1.59E+01
2.91 E+02
427E+02
400E 02
450E+02
8.77E*01
1.11E+03
1.45E*02
1.79E+03
563E+03
Average
QNB
Score
NoRfD
No RIO
NoR»D
No RID
No RID
No RID
NoRfD
NoRfO
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
NoRfD
No RID
NoRfD
NoRfD
No RID
NoRfD
390E+06
TOTAL COUNT =
Chemical Retained'
Cancer Nnn-cancer
Effects Effects

C

C
C


C
C
C
C
C
C
C
C
C
C
C
C
C
C
C
C
C

27 6
  >lume V, Appendix V-2
-------
                              APPENDIX V-3

                   Physical/Chemical Values Used to Estimate
                           Partitioning onto Particles
Volume V
Annpnriiv V-7
-------
 Table 1  Vapor/Particle Partmoning Factors for Stack Surrogate Chemicals
Chemical
2 3 7.B-TCDD
1.2.3.7.8-PCDD
1234 7.8-HxCDD
1.2.3,6,7.8-HxCDD
1.2,378.9-HxCDD
1,2,34,6,7.8-HpCDD
OCDD
2.3.7.8-TCDF
1.2,3,7,6-PCDF
2.347.8-PCDF
1.234.7.8-HxCDF
1. 2.3,6 7.8-HxCDF
1. 2,3.7 8.9-HxCDF
2.3.4.6.7 8-HxCDF
1.2.3.4678-HpCDF
1,2 347 B 9-HpCDF
OCDF
T etrachlorobtpnenyl
hexachlorobipnenyl
HeptachloroDiphenyl
Benzo(ajpyrene
Benzo(b)fluorantr>ene
Bis(2-ethy1hexyt)phtnalate
Carbon tetracnionde
ibenzl a, h (antnracene
-(Ji(n)octyl phtnaiate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclooentadiene
Hexachloropnene
lnoeno(1.2 3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Caomium
Chromium (hexavaient)
Lead
Mercury
Nickel
Selenium
Silver
Thallium
Zinc
Vapor
Pressure
mm Hg
7 40E-10
948E-10
1.01E-10
3.60E-11
4 90E-1 1
3.21 E-11
8.25E-13
8.96E-09
2 72E-09
3.29E-09
240E-10
2.20E-10
2.80E-10
2.00E-10
1.33E-10
1.07E-10
3 75E-12
2 80E-10
1.50E-06
3 OOE-07
5 49E-09
5 OOE-07
1.50E-07
1 14E+02
1.00E-10
1 40E-04
4.00E-04
1 90E-05
1 50E-01
8 OOE-02
not signrf (d)
1 OOE-10
(e)
(e)
(e)
(e)
(e)
(e)
(e)
2 OOE-03
(e)
(e)
(«)
(e)
(e)
Melting
Point
degree C (a)
306
241
274
286
244
265
326
228
226
196
226
233
248
240
237
222
259
453
414
431
179
168
-50
-23
266
-25
95.5
231
-21
-9
164
530
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
NR
Partitioning
Factor (D.
0449
C74"
0 925
0 964
098*
098C
0998
029i
0583
0697
0941
0936
-• 0 892
0933
0957
0 975
0998
0066
0000
0000
0673
0028
0751
0.000
1 000 (c)
0003
0.000
0000
0000
0000
1 000
1 000 (c)
1 000
1 000
1 000
1.000
1 000
1.000
1 000
0.000
1.000
1.000
1.000
1.000
1.000
(b)
(c)
(d)
NOTES
 NR = Not reauired to estimate the partitioning factor
 la) = The memng point is used m estimating the partitioning factor if it s greater than ambient temperature (20 degree C)
    = Fraction partitioning onto particle
    = PAHs with very low vapor pressures are assumed to be emitted as particles.
    = The literature qualitatively states that the vapor pressure for this chemical is "not significant"
       The vapor pressure is assumed to equal 0
 ~e) = All inorganic chemicals except mercury are assumed to be emitted as particles,
       therefore, a vapor pressure is not required
 Other constants needed to estimate the partitioning factor
                       St =  3.5E-06  cmA2/cmA3
                         c =  1.7E-04  atm-cm
                 delta Sf/R =     6 79  unrBess
                         T =     293  K
-------
                              APPENDIX V-4

             Physical/Chemical Parameter Values and Toxicity Values
                Used in Selection of Surrogate Organic Chemicals
                              (Fugitive Emissions)
Volume V
-------
 Waste Stream Constituent
 Acetone
 Acetonitnle
 Acetophenone
 Acetylammofluorene. 2-
 Acrylonitrile
 Alcohols
 Aliphatic hydrocarbons
 Aniline
 Benzene
 Benzenedicarboxylic acid, 1,2-
 Benzidme
 Benzoquinone, para-
 Benzo(a)pyrene
 Butanol
 Butyl acetate
 Calcium chromate
 Carbon
 Carbon disulfide
 Carbon tetrachloride
 Chlorobenzene
 Chloroform
 Chlor. paraffin, ,oil, wax
 Chrysene
 Creosote (coal tar)
 Cresol
 Crotonaldehyde
 Cumene
 Cyclohexane
 Cyclohexanone
 Dibenz(a,h)anthracene
 Dibromoethane
 Dichlorobenzene
 Dichlorodifluoroethane
 Dichlorodifluoromethane
 Dichloroethane (ethylidene dichloride
 Dichloroethene
 Diethyl stilbestrol
 Diethylphthalate
 Dimethyl sulfate
 Dimethylamme
 Dimethylbenzidme, 3,3'-
 Dimethylhydrazine
 Dimethylphenol
 Dimethylphthalate
 Dinitrotoluene
 Dioxane, 1,4-
Feed
Rate
(Ib/yr)
555858
78284
66350
71943
54259
338208
3208730
36020
174406
40427
55116
32012
33257
464645
39330
54606
149376
45647
104285
76207
90589
141435
33256
110180
1177104
37304
99450
144739
482451
32012
33724
206838
49180
58810
36854
49317
31397
122429
37304
44654
32012
34261
53872
93352
79191
107045

Molecular
Weight
58.1
41.1
120.1
223.3
53.1
53.9
114.0
93.1
78.1
166.1
184.2
108.1
252.3
74.1
116.2
156.0
12.0
76.1
153.8
112.6
119.4
623.0
228.2
184.4
108.1
70.1
120.2
84.2
98.2
278.4
187.9
147.0
135.0
102.9
99.0
97.0
268.3
222.2
126.1
45.1
212.3
60.1
122.2
194.2
182.1
88.1

Vapor
Pressure
231 a
88.8 a
0.397 a
—
107.8. a
30
14.1 a
0.489 a
95.2 a
—
0.83 c
—
5.5E-09 c
7 a
12.5 a
1E-06
1E-06
297 a
113.8 a
11.9 a
246 a
1E-06
6.3E-09 c
1E-06
0.31 a
19 b
10 b
97.6 a
4.8 a
1E-10 b
14 c
2.3 a
—
5013 c
227 a
591 a
—
1.65E-03 a
—
—
—
20.93 b
0.098 a
1.65E-03 a
3.5E-04 a
38 a

Temp
rc)
25
25
25

25


25
25

20

25
25
25


25
25
25
25

25

25
20
38.3
25
25
25
25
25

25
25
25

25



25
25,,
25
20
25

Slope
Factor
na
na
na
na
24E-01
na
na
na
2.9E-02
na
2.3E+02
na
na
na
na
na
na
na
5.3E-02
na
8.1E-02
na
na
na
na
na
na
na
na
na
7.6E-01
na
na
na
9.1E-02
1 .2E+00
4.9E+02
na
na
na
na
na
na
na
na
na

Reference
Dose
1.0E-01
1 4E-02
1.0E-01
na
5 7E-04
na
na
2 9E-04
na
1.0E+00
3.0E-03
na
na
1.0E-01
5.0E-02
na
na
3.0E-03
7.0E-04
5.7E-03
1 .OE-02
na
na
na
5.0E-03
na
2.6E-03
na
5.0E+00
na
5.7E-05
5.7E-02
na
5.7E-02
1.4E-01
9.0E-03
na
8.0E-01
na
na
na
na
6.0E-04
na
1 .OE-03
na
\/nh imo V  AnnonHiv \/_/
-------
Waste Stream Constituent
Epichlorohydrin
Ethanol
Ethoxyethanol, 2-
Ethyl acrylate
Ethylbenzene
Fiuoranthene
Formaldehyde
Formic acid
Furfural
Heptane
Hydrazme
lndeno(1,2.3-cd)pyrene
Isobutanol
Isopropanol
Isosafrole
Maleic anhydride
MEK (2-Butanone)
Methanol
Methyl methacrylate
Methylbutadiene, 1-
Methylcholanthrene, 3-
MIBK (2-Methyl-4-pentanone)
Naphthalene
Naphthylamme, 1-
Naphthylamine, 2-
Nitrobenzene
Nitrophenol (para)
Nrtropropane, 2-
N-nitrosodiethanolamme
N-nttrosodiethylamine
N-nitrosodi-n-butylamme
N-nrtrosopyrolidme
Phenol
Phthalic anhydride •
Picoline, 2-
Pyridme
Resorcmol
Tetrachlorobenzene
Tetrachloroethane
Tetrachloroethene
Tetrahydofuran
Toluene
Toluene diisocyanate
Toluenediamine
Trichloro-1,2,2,-trifluoroethane, 1,1,2
Trichlorobenzene
Feed
Rate
(Ib/yr)
52628
98523
351715
466761
364159
32012
100677
69352
57915
178323
38412
32012
238633
72266
35777
59443
676259
586938
71012
32012
32012
422393
92408
36583
38548
382090
32012
321555
51860
33339
32482
38548
84824
44878
32012
354015
57438
410043
50480
88399
125396
770291
50350
51594
85377
44001

Molecular
Weight
92.5
46.7
90.1
100.1
106.2
202.3
30.0
46.0
96.1
100.2
32.1
276.3
74.1
60.1
162.2
98.1
72.1
32.0
100.1
68.0
268.4
100.2
128.2
143.2
143.2
123.1
139.1
89.1
134.1
102.1
158.3
100.1
94.1
148.1
93.1
79.1
110.1
220.0
167.9
165.8
72.1
92.1
174.2
122.2
187.4
181.5

Vapor
Pressure
16.44 a
59 a
5.3 b
29.3 b
9.53 a
5E-06 c
3883 a
35 b
2.5 a
45.8 a
14.4 b
1E-10 c
10.4 a
43 a
—
0.41 a
90.6 a
92 a
38.4 a
—
—
14.5 a
0.082 a
—
—
0.15 a
—
20 b
5E-04 b
0.86 b
0.03 b
0.01 b
0.524 a
2E-04 a
—
20 a
—
4.5E-02 d
12 a
18.5 a
162.3 a
28.4 a
—
5.2E-05 a
362.5 a
5.8E-01 a

Temp
CC)
25
25
25
20
25
25
25
20
25
25
25
25
25
25

25
25
25
25


20
25


25

25
20
20
20
25
25
20

25

25
25
25
25
25

20
25
25

Slope
Factor
4.2E-03
na
na
na
na
na
4.5E-02
na
na
na
1.7E+01
na
na
na
na
na
na
na
na
na
na
na
na
na
na
na
na
9.4E+00
na
1.5E+02
5.4E+00
2.1E+00
na
na
na
na
na
na
2.0E-01
5.2E-02
na
na
na
na
na
na

Reference
Dose
2.0E-03
na
5.7E-02
na
2 9E-01
4 OE-02
2.0E-01
20E+00
1 4E-02
na
na
na
3 OE-01
na
na
1 OE-01
2.9E-01
5.0E-01
2.3E-02
na
na
8.0E-02
4. OE-02
na
na
5.7E-04
na
5 7E-03
na
na
na
na
6.0E-01
3.4E-02
na
1 .OE-03
na
3.0E-04
3. OE-02
1 .OE-02
na
1.1E-01
na
na
8.6E+00
5.7E-02
Volume V  Annpnriiv \/.A
-------
  /Vaste Stream Constituent
  Trichloroethane,  1,1,1-
  Trichioroethylene
  Tnchlorofluoromethane
  Xylene
Feed
Rate
(Ib/yr)
153251
100350
69874
448321

Molecular
Weight
133.4
131.4
137.4
106.2

Vapor
Pressure
123.7
69 a
803 a
8.7 a

Temp
(°C)

25
25
25

Slope
Factor
na
1.1E-02
na
na

Reference
Dose
na
na
2.0E-01
2.0E+00
  Notes
  a - Howard 1993, b - HSDB, c - Montgomery & Welkom 1990, d - calculated based on Grayson 1984. e - assumed to be insignificant  1 E-6
  Feed rates estimated from first year of operation, as described in Appendix 111-1
  Slope factors and reference doses obtained from IRIS (1995) and U.S EPA (1994)
  -  For substances without a slope factor or reference dose, a vapor pressure was not necessarily identified
Volume V Aooendiy V-
-------
                              REFERENCES
 Grayson, M. (Ed.)  1984.  Kirk-Othmer.  Encyclopedia of Chemical Technolog\. 3rd
       Edition. Wiley-Interscience.  John Wiley & Sons. New York.

 Hazardous Substance Data Base (HSDB).  On-line data base of physical-chemical
       information.

 Howard. P.H.  1993.  Handbook of Environmental Fate and Exposure Data for Organic
       Chemicals.  Lewis Publishers.  Chelsea, Michigan.

 Integrated Risk Information System (IRIS). 1995. U.S. Environmental Protection Agency's
       on-line data base.

 Montgomery, J.H. and L.M. Welkom.  1990.  Groundwater chemical desk reference.  Lewis
       Publishers.  Chelsea, Michigan.

 United States Environmental Protection Agency (U.S. EPA).  1994.  Health effects
       assessment summary tables, FY-1994 annual update.  Office of Research and
       Development, Office of Emergency and Remedial  Response.  EPA 540-R-94-020.
       March.
Volume V
Appendix V-4
-------
                            APPENDIX V-5



                 Evaluation of Additional High-end Subgroups
Volume V
-------
INTRODUCTION

       The WTI Risk Assessment Project Plan identifies a number of subgroups of the
population that may be exposed directly or indirectly to emissions from the facility.
including:

       •      Adult non-farming residents living in homes with gardens:
       •      Child non-farming residents living in homes with gardens:
       •      Adult non-farming residents living in homes without gardens:
       •      Child non-farming residents living in homes without gardens;
       •      Adult farmers whose diet consists partially of homegrown food products
              (e.g., meat, milk, vegetables);
       •      Farm children whose diet consists partially of homegrown food products:
       •      Adult farmers whose entire diet is  homegrown (referred to as subsistence
              farmers);  and,
       •      Subsistence farm children.

       In addition to these subgroups, groups of individuals are identified as  members of a
special population segment or individuals who may be highly exposed because of their
particular activity patterns.  These groups include:

       •      Children (7 to 12 years old) who attend school in the area;
       •      Breast-feeding infants (assumed to  be all children under 1 year old): and,
       •      Subsistence fishermen (recreational fishermen who obtain a significant portion
              of their diet from fish in local bodies of water).

       During the peer review process conducted for the WTI Risk Assessment Project Plan,
the Exposure Assessment Work Group identified  a  number of additional subgroups of the
exposed population that may be at a higher risk due to behavior patterns, proximity to the
facility, or sensitivity. The purpose of this appendix is to evaluate each of the potential
subgroups identified by the Exposure Assessment Work Group  and provide a rationale for
omitting or including each subgroup in the exposure assessment for the, WTI Risk
Assessment.
Volume V
Appendix V-5
-------
EVALUATION OF ADDITIONAL HIGH-END SUBGROUPS

       The Exposure Assessment Work Group of the peer review committee indicated that
the following subgroups should be evaluated for inclusion in the WTI Risk Assessment:

       •     Children who live near the facility and attend school near the faciliu:
       •     Individuals who work at WTI;
       •     Adults who live and work near WTI;
       •     Elderly individuals in the study area;
       •     Hunters of deer and waterfowl; and,
       •     Other potentially high-end exposure  subgroups.

The rationale for including or omitting each of these subgroups is provided in the following
sections.

Children Who Live and Attend School Near the Facility

       As noted earlier, the proposed methodology for estimating exposure accounts for
varying activity and behavior patterns by dividing the exposed population into 11 subgroups
and accounts for location with  respect to the WTI facility by identifying isoconcentration
subareas.  One of the subgroups of the exposed population identified in the WTI  Project Plan
is children (7 to  12 years old) who attend school in the area.  This exposure  subgroup was
developed to include children living and attending school in the study area and will include
children in subareas near the facility and farther away.  Therefore, this additional subgroup
is already included in the subgroups identified in the Project
Plan.

Individuals Who Work at WTI

       It is possible that individuals who work at the WTI facility may be exposed to
chemicals in the workplace which may result in incidental transport of contaminants to off-
site locations, resulting in potential exposures to off-site individuals (e.g., family members).
Quantitative evaluation of worker exposure and transport of chemicals off-site by workers is
beyond the scope of the WTI Risk Assessment, however, WTI worker exposure and
migration of contaminants by workers are  addressed qualitatively in the uncertainty section of
the WTI Risk Assessment.
Volume V
Appendix V-5
-------
Adults Who Work and Live Near WTI

       Adult residents living and working in the study area are one of the population
subgroups identified in the WTI Project Plan. Exposure factors for this subgroup reflect the
possibility that an individual may be exposed to emissions from the WTI facility either at
home or at a place of employment.   Therefore, this subgroup is already included in the
subgroups identified in the Project Plan.

Elderly Individuals

       The peer reviewers noted that the population in the vicinity of the WTI facility has a
higher than expected concentration of elderly individuals; therefore, the  reviewers
recommended that this subgroup be considered for inclusion in the WTI Risk Assessment.
Based on a review of 1990 census data for the counties in the vicinity of the WTI facility.
elderly populations do not appear to be above average.
       In addition, based solely on activity patterns or location, there is no reason  to  believe
that elderly individuals will necessarily be on the high-end of the exposure distribution.
unless specific activities (e.g., subsistence fishing, subsistence farming) cause them to be
exposed to a greater degree than other population subgroups.  These types of potentially
high-exposure activities are considered in the WTI Project Plan; therefore, a specific
subgroup for elderly individuals is not warranted.
       It is possible that elderly individuals may be on the high-end of the risk distribution
because of a higher than expected sensitivity to contaminants to which they may  be exposed.
Toxicological  data are not available, however, to effectively evaluate elevated sensitivity to
chemicals by elderly individuals as a separate analysis.  Consequently, estimates  of
lexicological potency incorporate safety factors to account for the presence of sensitive
individuals in  the population (e.g.,  elderly people).  Therefore, this  subgroup is not
considered separately in the WTI Risk Assessment.

Hunters of Deer and Waterfowl

      It is possible that deer and waterfowl that live  in the study area may be exposed to
contaminants emitted from the WTI facility.  Potential effects  to such species are be
addressed in the Sceening Ecological Risk Assessment for the WTI facility.  As part of the
exposure assessment for the WTI Risk Assessment,  hunters  who may be exposed indirectly
to facility emissions due to consumption of exposed deer or waterfowl are evaluated
qualitatively to estimate the likelihood that this type of exposure is significant (i.e., more

Volume V
Appendix V-5
-------
 significant than exposure by other food consumption pathways, such as subsistence beef or
 fish consumption).  For example, estimates of deer hunting in the vicinity of the WTI facilit)
 are developed to evaluate the  likelihood that deer meat consumption may be  of a greater
 concern than beef consumption.  It is unlikely, however, that this subgroup will be exposed
 to a significantly greater degree than other high-end subgroups such as the subsistence
 farmer.

 Other Potentially High-end Exposure Subgroups

       No additional potential exposure subgroups were identified that may be exposed
 significantly but were not adequately represented by subgroups considered in the WTI Risk
 Assessment.  It is believed that the exposure subgroups evaluated in the  WTI Risk
 Assessment largely reflect the population in the study area and addition of other groups
 would not substantially  alter the results of the assessment.

 SUMMARY

       Based on the peer review of the WTI Project Plan, several possible additional high-
 end exposure subgroups were  identified. Each of the recommended subgroups were
 evaluated  regarding possible inclusion in the WTI Risk Assessment, with the following
 results:

 1)     Children who live and  attend school  near the facility - This  subgroup  is already
       considered in the WTI  Project Plan.
2)     Adults who work at WTI - Quantitative assessment of exposure to workers at the WTI
       facility itself is beyond the scope of the WTI Risk  Assessment, but is discussed
       qualitatively in the WTI Risk Assessment.
3)     Adults who work and live near WTI - Adult residents are identified in the Project
       Plan and exposure to emissions from WTI, regardless of location (i.e., work, home,
       or  school), is evaluated for this subgroup.
4)     Elderly individuals -  Elderly individuals are  not necessarily at the high-end of the
       exposure distribution, and although elderly people may be at the high-end of the risk
       distribution due to increased lexicological sensitivity,  such increased sensitivity is
       accounted for in the Toxicological Assessment.
5)    Hunters of deer and waterfowl - It is possible that  hunters who kill and consume deer
       or  waterfowl from the study area may be exposed to emissions from the WTI facility.
       It is unlikely, however, that this type of exposure will be greater  than exposure from

Volume V
Aonendiv  V-S
-------
         other potentially high-end activities (e.g.. subsistence fishing or farming).
         Nonetheless, a qualitative analysis is performed as pan of the WTI Risk Assessment
         to evaluate the possible addition of this subgroup.
  6)      Other potentially high-end exposure subgroups  - No additional potential high-end
         exposure population subgroups  were identified.  The subgroups identified in the  WTI
         Project Plan are believed to include a significant fraction of the exposed population in
         the study area.
Volume V
-------
                             APPENDIX V-6



             Evaluation of Residential Exposure to Locally Caught Fish
Volume V
-------
 RECREATIONAL FISHING DATA

        The state Departments of Natural Resources (DNR) in Ohio. West Virginia, and
 Pennsylvania were contacted to obtain recreational fishing data.  Two recently conducted
 recreational fishing studies were identified: 1) a joint study conducted in  1992 by the Ohio
 DNR and West Virginia DNR (ODNR 1994a); and 2) a study being conducted for the
 Pennsylvania DNR (Terrestrial Environmental Systems 1994). Sufficient data to estimate the
 number of anglers or typical fish harvest in this area were not available from the
 Pennsylvania study at the time of this assessment.

        The joint Ohio/West Virginia DNR recreational fishing study (ODNR 1994a) was
 conducted to identify the amount of fishing and the types of fish  being caught along the Ohio
 River between  the Ohio/Pennsylvania border (Ohio River Mile 40.1) and  Greenup Dam. 300
 miles downstream (ORM 341). This 300-mile study area was subdivided into 32 survey
 areas, which include survey points  (embayments and tailwaters),  and pools.   Four of the 32
 survey  areas  (locations #1 to #4) are in the general vicinity (30-kilometer radius) of the WTI
 facility  (located at ORM 41.5). These four survey areas are assumed to be  representative  of
 the Ohio River in the vicinity of the WTI facility. The four survey areas  cover the entire
 stretch of the Ohio River from the  Ohio/Pennsylvania border to Steubenville, Ohio (ORM
 40.1 to  ORM 69.5). Data from survey areas located farther down river (ORM 69.5 to ORM
 341) are also evaluated as a basis for comparison.

      The DNR study was conducted between April and November 1992.  Very little
 fishing occurs between December and March; therefore, the data  collected in this study are
 assumed to reflect annual data.  Table 1 summarizes the recreational fishing data obtained
 from  the Ohio/West Virginia DNR  study (ODNR 1994a).

 RESULTS

      Although the Ohio/West Virginia DNR study provides significant data concerning the
types  of fish being caught and kept  along the Ohio River, sufficient data are not  available to
characterize the relationship between fishing practices and fish consumption by the  local
population.  However, data contained in the Ohio/West Virginia DNR "study and information
Volume V
Appendix V-6
-------
TABLE 1
Summary of Ohio River Recreational Fishing Study Data
Parameter
Estimated Number of Fish Caughf
Estimated Number of Fish Kept*
Estimated Number of Angler Hours3
WTI Facility
Vicinity"
400,000
63,000
180,000
Farther
Downstream
of WTI
2.800.000
300.000
1.600.000
Fish Type and Size Data for Survey Locations in WTI Vicinity
Types of Fish
Bass
Percids
Catfish
Carp
Other
% of Fish
Kept
88%
8%
1%
<0.1%
3%
Avg. SizeJ
finches)
7 - 13
11 - 13
12 - 17
17- 18
6- 16
Notes:
a - Values extrapolated by ODNR (1994a) from raw data. The number of angler hours were
estimated based on a count of anglers on the Ohio River over a specified time period.
b - Represents data collected in ODNR (1994a) study from survey areas #1 to #4 (Ohio River Mile
(ORM) 40.1 to 69.5). The WTI facility is at ORM 41.5.
c - Represents data collected in ODNR (1994a) study from survey areas #5 to #32 (ORM 69.5 to
341).
d - Approximated from fish length data compiled by ODNR (1994a).
Volume V
Appendix V-6
-------
obtained from local fish and wildlife agencies indicate that fish raised in the vicinity of the
WTI facility are not a significant source of food for the typical local resident1.  Information
used to support this assessment include the following:

•      No commercial fishing operations operate in the vicinity of the WTI facilin.
       Fish and wildlife agencies in Ohio, West Virginia, and Pennsylvania were contacted
       regarding the presence of commercial fishing (i.e., operations or individuals that catch
       fish and distribute to local supermarkets  and restaurants) in the vicinity of the WTI
       facility (ODNR 1994b; West Virginia Fisheries  1994;  PFBC 1994a).   Although
       several fish farms are located in the general vicinity of WTI, the fish and wildlife
       officers contacted indicated that the fish  raised in these operations are  not sold for
       consumption, but are used as stock fish in local  water  bodies.  None of the officials
       contacted had any knowledge of any commercial fishing operations in  the WTI area:
       therefore, all local fish consumption must be derived from fish caught by individual
       fishermen.

•      Only a small fraction of the resident population in the  vicinity of WTI fish.
       Agencies in Ohio (ODNR 1994c), West  Virginia (WVDNR 1994), and Pennsylvania
       (PFBC 1994b) responsible for fishing licenses were contacted for information
       regarding the number of fishing b'censes  sold in  counties  surrounding the WTI
       facility. Based on data provided by  these agencies,  the total number of annual
       resident fishing licenses in the 11 counties surrounding the WTI facility is
       approximately 180,000. The total population in  these 11 counties is over 2.5 million.
       based on 1990 census data.  Therefore, approximately  seven percent of the population
       in the WTI area is legally permitted  to fish.  Although it is possible that some
       individuals may fish without a license,  survey data collected in the Ohio/West
       Virginia DNR fishing study  (ODNR 1994a) indicate  that only  3 percent of the anglers
       surveyed did not have licenses. Although these individuals who fish will be exposed,
       these data indicate that a significant fraction of the entire local population does not
       fish; therefore, it is unlikely that a significant fraction of their fish diet is derived
       from local sources (i.e., an average individual's  fish diet does not contain a
       significant fraction of locally caught fish).  As noted earlier, risks to the fishing
       population are represented in this assessment by  the subsistence fisherman scenario.
    1 This is not meant to imply that subsistence fishing is or is not occurring in this area.
Subsistence fishermen are considered separately from local residents in the WTI Risk
Assessment.

Volume V
Appendix V-6                               i
-------
       The amount of fish caught locally and kept is unlikely to be significant.
       According to the results of the Ohio/West  Virginia DNR study (ODNR 1994a).
       approximately 400,000 fish were caught and 63,000 fish were kept along the 30 miles
       of the Ohio River between the Ohio/Pennsylvania border and Steubenville. Ohio
       during 1992.  As indicated in Table 1, almost 90 percent of the fish kept by anglers
       were of the bass family, which are generally relatively small fish (fish size data
       collected during the ODNR study indicates an average bass length of between 7 and
       13 inches). The Ohio River Valley Sanitation Commission (ORSANCO) conducted
       an electrofishing survey (between ORM 21.6 and ORM 55.5) during 1991 to 1993
       (ORSANCO 1994) that provides the average weight of fish from the Ohio River
       corresponding to various size ranges.  Based on these data, it is estimated that fish in
       the size ranges provided in Table 1 range from 50 to 650 g (0.1 to 1.4 pounds) with
       an average of 180 g (0.4 pounds).  As a conservative estimate,  it is assumed that the
       average fish caught along the Ohio River yields no  more than 0.4 pound of fish for
       consumption. The 63,000 fish caught along the 30 miles of the Ohio  River (survey
       locations #1 to #4) in the vicinity of WTI in 1992, therefore, resulted in no more than
       25,000 pounds of fish per year available for consumption. Even if the high-end of
       the weight range is assumed, no more than 90,000 pounds of fish per year from the
       Ohio River is available for consumption. The 25,000 pounds of fish caught locally.
       therefore, corresponds to less than 0.2 grams of fish consumed  per day for the fishing
       population (based on the number of fishing licenses and assuming the fish is not
       distributed amongst a larger population). Furthermore, the 25,000 pounds of fish
       corresponds to less than 0.01 g/day of locally caught fish for local residents
       (assuming the fish is distributed evenly amongst all  local residents  in the 11 -county
       area near WTI).  These consumption rates of locally caught fish are insignificant
       compared to the average fish consumption rate of 11 g/day for residents.
       It should be noted that fishing is likely to occur at locations throughout the area
around the facility (i.e., other than the Ohio River), including smaller rivers, lakes, and
ponds.  Discussions with local fish and wildlife officers (ODNR 1994b; West Virginia
Fisheries 1994; PFBC 1994a) indicate, however, that the Ohio River is likely to be the most
significant source of fishing in the area.  Therefore, considering the approximate size of the
fishing population (180,000) and the local population  (approximately 2.5 million), it does not
                                                                  f
appear that a significant fraction of local residents' fish diet comes from fish caught locally.
Volume V
Appendix V-6
-------
       In summary, the data available from the Ohio/West Virginia DNR fishing study
 (ODNR 1994a) and the information obtained from discussions with fish and wildlife officials
 familiar with fishing practices  in the vicinity of the WTI facility indicate that fish from local
 waters are unlikely to contribute a significant fraction of the fish diet for local  residents.
 Therefore, exposure to contaminants that are released from the WTI facility and
 bioaccumulate in fish are not considered in the WTI Risk Assessment as a potential exposure
 pathway for the typical local resident.  However, because individuals may exist in the stud\
 area who represent high-end exposure to contaminants in fish, a subsistence fisherman
 scenario is considered in the Risk Assessment.  Uncertainties associated with not including
 the resident fish consumption exposure pathway are discussed in the uncertainties section of
 the Risk Assessment.  An additional  source of uncertainty may  arise because this assessment
 is not designed to estimate contaminant exposure to individuals  who consume a specific
 species of fish (e.g., carp) as a predominant portion of their diet.  Although certain species
 (e.g., carp) may have a relatively greater lipid content, resulting in relatively higher
 contaminant  concentrations, this assessment estimates concentrations of contaminants in fish
 based upon a reasonable estimate of several factors, including the lipid content  of fresh water
 fish.
Volume V
Appendix V-6
-------
                                 REFERENCES
A.T. Kearney, Inc. (ATK).  1993.  W77 phase II risk assessment project plan. Prepared for
      the United States Environmental Protection Agency. Region 5. Chicago. U.S. EPA
      Contract No. 68-W9-0040. November.

Ohio Department of Natural Resources (ODNR).  1994a.  Ohio River recreational use snn-e\
      1992 survey. Preliminary results.  State Project F4DR03.  March.

Ohio Department of Natural Resources (ODNR).  1994b.  Personal communication, V.
      LaConte, District Fish Management Supervisor.  December 15.

Ohio Department of Natural Resources (ODNR).  1994c.  Personal communication.
      Division of Wildlife.  November 2.

Ohio River Valley Water Sanitation Commission (ORSANCO).  1994. Personal
      communication, L.D.  Boggs, Aquatic Biologist.  September 9.

Pennsylvania Fish and Boat Commission (PFBC).  1994a.  Personal communication, R.
      Lorson. December 19.

Pennsylvania Fish and Boat Commission (PFBC).  1994b.  Personal communication.
      November 2.

Pierce, B.E., C.W. Stihler and T.E. Cheek.  1983. A recreational use survey of the Ohio
      River in West Virginia.  West Virginia Department  of Natural Resources, Division of
      Wildlife Resources, Charleston, West Virginia.

Terrestrial Environmental Systems. Inc.  1994.  Personal communication, C.A.
      Baumgartner. November 4.

U.S. Environmental Protection Agency.  (U.S. EPA). 1990.  Exposure factors handbook.
      Office of Health and Environmental Assessment,  Washington, D.C.  U.S.
      EPA/600/8-89/043.

West Virginia District Fisheries.  1994.  Personal communication, F. Jernejcic, Biologist.
      December 15.

West Virginia Department of Natural Resource (WVDNR). 1994. Personal communication,
      A. Johansen, Wildlife Resources Section.  November  10.
Volume V
Appendix V-6
-------
                           APPENDIX V-7





            Fate and Transport Model Equations and Parameter Values
Volume V
-------
                                    APPENDIX V-7
              Fate and Transport Model Equations and Parameters Values
Overview
     Receptors are exposed to stack gas chemicals by both direct and indirect pathways.
Direct exposure occurs through inhalation of vapors and particles in the air. Indirect exposure
occurs as a result of dry and wet deposition of particles and vapor onto the soil, migration of
chemicals into vegetation, animals, and surface water, and subsequent human ingestion of soil.
vegetation, animal products, fish, and surface water that has been affected by stack gas
emissions.  Exposure concentrations in affected media are estimated using fate and transport
models that simulate the transport of stack gas chemicals in the environment. These models
are based on U.S. EPA (1990a, 1993, and 1994a) guidance; however, it should be noted that,
in several cases, the chemical fate and transport models are based on limited data.  The
uncertainties in applying these models to a broad spectrum of chemicals are discussed in the
uncertainty section of the Human Health Risk Assessment.
     This appendix presents the fate and transport model equations and inputs used to estimate
environmental concentrations.  Site-specific values are used wherever possible, otherwise,
U.S. EPA recommended  default parameters are used.  This appendix  is  divided into six
sections, corresponding to the six different media for which concentrations  are needed to
estimate indirect human health risks: 1) soil, 2) vegetation, 3) meat, eggs, and milk, 4) surface
water,  5) fish, and 6) mothers' milk.  Physical/chemical values for the chemicals of concern
and site-specific parameters are presented in Tables 1 to 4. It should be noted that because
mercury is assumed to exist as a vapor, additional parameters are required to evaluate its fate
and transport.  These parameters are listed in the footnote  in Table 3.
     As discussed in Volume n, the key assumptions that  are used in performing the WTI Risk
Assessment are identified. Table 38 summarizes  the key assumptions that are used in
developing  estimates of exposure concentrations in the various media. The table indicates the
basis for the assumptions  listed, the estimated  relative magnitude of the assumption's effect  on
the overall risk assessment, and the direction of the effect, if known.
Volume V
Appendix V-7
-------
Table I
Chemical-specific Parameters for Dioxiu-like Compounds
Compound
2,3,7,8 TCDD
1,2,3,7,8 PeCDD
1,2,3,4,7,8 HxCDD

1,2,3,6,7,8 HxCDD
1,2,3,7,8,9 HxCDD
1,2,3,4,6,7,8 HpCDD
ocpn
2,3,7,8TCDF
1,2,3,7,8-PeCDF
2,3,4,7,8-PeCDF
1,2,3,4,7,8 HxCDF
1,2,3,6,7,8 HxCDF
TEF
t Oa
05a
0 1 B
0 1 a
0 1 a
001 a
0 001 a
O.I t
0.05 a
0 5 a
0 1 a
0 1 a
Molecular
Formula
C^H.CIA
C,,H,CI502
c.^ci.o,
cWi.o,
c-,,H,ci6o:
C,,HCIA
cac\,o,
C^H.CI.O,
C.iHjCI.O,
C^H.CIA
CaH,CI60,
C,2H,CI,0,
Molecular
Weight
321 98 a
356 42 a
390. 87 «
390.87 a
390 87 a
425 31 a
460.76 a
305 98 a
340 42 a
340.42 a
374 87 a
374 87 a
log
Kow
664 a
6.64 a
7.79 a
7 30 a
7 79 a
8.20«
7 59 «
6.53 a
6.79 a
6 92 a
7 30 a
7 30 a
Koc'
L/kg or cm'/g
2 7x 10' •
27x 10'«
3 8 x 107 *
1 2 x 10' a
1 2 x 10' >
9 8 x 10' a
2 4 x 10' a
2 1 x 10' a
3 8 x 10' a
5 1 x 10' i
I 2 x 10' a
1 2 x 101 a
II
nlm-ii^/iiiol
1 6 x 10'a
2.6x 10'a
1.2 x 10'a
1.2 x 10'a
1 2 x 105a
75x I06a
70x 10'a
8 6 x 10'a
62 x I06a
62 x 10'a
1.4 x I0'a
6 1 x 10'a
Animal
Fal BCF
4.32 a
4.l6a
2.02 a
1.74 a
2 24 a
0.36 a
0.52 a
0.94 a
0.73 a
3. 10 a
2 34 a
2 00 a
BSAF
009 a
009 a
0.048
0.04 a
004 a
0005 a
00001 a
009 a
009 a
009 a
004 a
004 «
Vapor P
nun llg
7.40 x 10%
9.48 x 10 '"a
1.01 x I0'°«
3.6 x I0"a
49 x I0"»
3.21 x I0"a
8.25 x 10 "a
8.96 x 10 '«
2.72 x 10'a
329 x 10' «
2 4 x 10 '"a
22 x 10 '"B
Melting
Point
"C
306 a
240 a
274 «
286 a
244 n
264 »
325 «
228 a
226 a
196 n
226 »
211 «
RCF
L/kg
3.9 x 10'a
3 9 x 10' a
3.0 x 10' «
1.3 x 10' a
1 3 x 10' »
6 2 x 10' a
2 1 x 10' a
3 2 x 10' a
5 1 x 10' a
6 4 x 10' a
1 1 x Id' »
11 x 10' »
Volume V
Appendix V-7
-------
Table 1
Chemical-specific Parameters fur Dioxin-like Compounds
Coin pound
1,2,3,7,8,9 HxCDF
2,3,4,6,7,8 HxCDF
1,2,3, 4,6,7, 8-HpCDF
1,2,3,4,7,8,9 HpCDF
OCDF
Tetachlorobiphenyl
Hexachlorobiphenyl
Heptachlorobiphenyl
TEF
O.I a
0 1 a
001 a
001 a
0001 a

-

Molecular
Formula
CnH.CI.O,
CaH,CltO,
C,,HCI,0,
C.jHC^O,
C.jCI.O,
C,,H(CI,
C,,H.CI,
CuH.CI,
Molecular
Weight
374 87 a
374 87 a
409 31 a
409.31 a
444 76 a
291 99 a
360 88 a
396 33 a
log
Kow
7.30 a
7 30 a
7.90 a
7.90 a
8 80 a
6 21 a
7 17a
7 7 a
Koc1
L/kg or cm'/g
1 2 x 10' a
1 2 x I07 a
4 9 x 10' a
4 9 x 10' a
3 9 x 10' a
8 46 x 10' b
3 21 x 10' b
1 41 x 10' b
II
ntm-m'/inol
l.Ox 10'a
1.0 x 10'a
5.3 x 10'a
5.3 x 10'a
1 9x 10'a
94 x 10'a
5 8 x 10'a
6 6 x 10'a
Animal
Fat BCF
2.00 a
1.78 a
0.41 a
0.99 a
0.20 a
5.9 a
2.2 a
2.3 a
BSAF
004 a
004 a
0005 a
0.005 a
0.0001 a
0.92 a
2.64 a
20a
Vapor P
mm llg
2 8 x 10'%
20 x 10 '" a
1.33 x 10 '"a
1.07 x 10'° a
3 75 x 10 "a
2.8 x I010a
1 5 x 10'a
3 Ox 10'a
Melting
Point
"C
248 n
240 a
236 a
222 a
259 a
453 a
414 a
431 a
RCF
L/kR
1 3 x 10' n
1 3 x 10' a
3 7 x 10' a
3 7 x 10' a
1 8 x 10' a
1 8 x 10' c
1 0 x 10' c
2 6 x 10' c
Volume V
Appendix V-7
-------
                                                                                   Tahle 1
                                                            Chemical-specific Parameters for Dioxin-like Compounds
       Compound
                           TEF
                                  Molecular
                                   Form ula
Molecular
 Weight
 log
Kow
    Koc'
L/kg or cmVg
     II
ntni-in'/mol
 Animal
Fat BCF
BSAF
Vapor P
mm llg
Melting
 Point
  "C
RCF
L/kR
  NOTES
   half life of dioxin in adults (h) = 2,555 days for 2,3,7,8 TCDD (d) and assumed for all other dioxin like compounds.
   proportion of ingested dioxin-like compound stored in fat (f,) = 09 for 2,3,7,8-TCDD (d) and assumed for all other dioxin like compounds.
   proportion of mother's weight that is fat (t\) = 0 3 kg fat/kg BW for 2,3,7,8-TCDD (d) and assumed for all other dioxin-like compounds.
   below ground vegetation correction factor (VO^  = 0.01 for 2,3,7,8-TCDD (d) and assumed for all other dioxin like compounds
   half-life on plant surfaces (I,,,) = 14 days for all dioxin-like compounds (a).
   soil degradation constant (ksg) = 0 0693 yr ' for all dioxin-like compounds (a).
   air diffusion coefficient (D.)  = 0 05 cmVsec for 2,3,7,8-TCDD and 2,3,7,8 TCDF (a) and for all other dioxin-like compounds (e).
   a   U S  EPA I994a
       V S. EPA 1983.
      calculated by ENVIRON
       U S  EPA 1993.
      calculated by the FSO method in Lyman el al 1992.
             oclanol/waler partition coefficient
             organic carbon adsorption  coefficient
             Henry's law constant
             hioconcentmtion factor
             biota to sediment accumulation factor
b
c
d
e
Kow
Koc
H
BCF
BSAF
Vapor P
RCF
              vapor pressure
              root concentration factor
       soil/water partition coefficient (KdJ =  Koc x fraction organic carbon in soil (OC^, see Table 4)
       suspended sediment/water partition coefficient (Kd_<) = Koc x fraction organic carbon in suspended sediment (OC_,, see Table 27)
Volume V
Appendix  V-7
-------
Table 2
Chemical-specific Parameters lor Organic Compounds
C nm pound
Benzo(a)pyrene
Benzo(h)fluoranthene
Bis(2-elhylhexyl)
phthalate
Carbon letrachloride
Dibenz(a,h)anlhracene
Di(n)oclyl phlhalale
Heptachlor
Hexachlorohenzene
Hexachlorohutadiene
Hexachlorocyclo-
pentadiene
V
Hexachlorophene
Indeno(l,2,3 cd)
pyrene
CAS#
5032-8
205-99-2
117-81-7
56 23-5
53 70-3
1 17 84 0
76 44-8
118-74-1
87-68-3
77-47-4
70 30-4
193 39-5
Molecular
Formula
C^H.,0
C»»n '
CMH,,0, h
CCI.h
CEH14 c
CMH,,0, e
C,0H,CI, b
C.CI, h
C.Cl.h
C,CI, e
CuH.CI.O, e
CnH,,c
Molecular
Weight
252 32 c
252.32 c
390 54 b
153 84 h
278 36 c
390 56 e
373 35 h
284 80 b
260 76 b
272 77 e
406 92 e
276 34 c
log
Knw
6 11 j
62j
73j
2.73J
669J
8 06j
6.26J
5 89 j
4 81 j
5 39j
7 54 j
6 65 j
Koc'
L/kg or
rui'/g
3 95 x 10" e
5 50 x 10' c
1 2 x I01 k
HOh
1 66 x 10' c
19,000 e
30,200 h
10,000 h
5,181 b
4,265 e
91, 000 h
1 6 x 10' h
II
nttn-in'/mol
1 55 x 10' f
1.19 x 10'h
27x 101!
3 04 x 10'b
7 x 10'e
5 5 x 10'e
1 48 x 10'b
1 3 x 10'b
1 03 x 10'b
2 7 x 10'e
5 48 x 10" e
6 86 x 10'h
Fish BAF1 (L/kg)
BCF
3,208m
3,208 n
886 p
30 q
51, 000 e
9,400m
23,814
m
39,000
m
.17,000 r
448 e
278 m
59,407 e
FCM"
17 783
19.907
22856
1.005
26.363
6 726
20.963
13.964
1.871
5821
18.080
26004
soil tw " (hr)
ksgHvr1)
1,368 - 12,720
1.46
8,640 - 14,640
0.540
120 - 550
23.6
4,320 - 8,640
0994
8,664 - 22,560
0.434
168 -672
18.1
23 1 - 129 4
111
23,256 -50,136
0.18
672 - 4,320
3.56
168 -672
18.1
6,000 - 7,872
0 884
14,400 17,520
0 182
n.'
cm'/sw
00513
00513
00373
0.0818
0.0479
00373
0.0488
00573
00594
00872
0 0454
0 0499
Vapor P
mm llg
5 49 x 10 'c
5 x 10'e
1 5 x 10 ' 1
113 8 l<
1 x I0'"e
1 4 x 10' c
4 x 10s h
1 9 x 10' b
0 15 h
0 080 e
mi sipiiilicnnl
volatilization e
1 0 x 10'" e
Volume V
Appendix V-7
-------
                                                                                  Table 2
                                                             Chemical-specific Parameters for Organic Compounds
       Compound
                           CAS 9
Molecular  .
 Formula
Molecular
 Weight
                                                                   Kow
 Koc1
L/kg or
 rin'/p
     II
alin-mVinol
Fish BAF' (L/kg)
                                                                                                          BCF
soil t% ' (hr)
  n.'
rm'/src
Vapor P
mm HR
  NOTES.
   a   Howard el al.  1991
   h   Howard 1989-1991.
   c   Montgomery & Welkom 1990
   d   calculated from the geometric mean of the soil half-lives and ksg = In 2/tM (g) unless
       otherwise noted
   e   HSDB
   f   U.S  EPA  1990s
   g   US. EPA  I994a.
   h   US. EPA  I990b
   i    calculated by the FSG method in Lyman et al  1992
   j    U S  EPA  I995a.
   k   calculated as \Q""tt" "J" (U S  EPA  1993)
   I    Mackay e( al  1995.
   m   US  EPA  AQU1RE data base
   n   No data so value for henzo(«)pyrene conservatively applied.
   o   U.S. EPA  1995H
   p   U.S. EPA  1980s
   q   U.S. EPA  I980b
   r    U S. EPA  1980
                                     plant t(<      plant-surface loss coefficient =  14 days for all compounds (g)
                                     Kow octanol/water partition coefficient
                                     Koc  organic carbon adsorption coefficient
                                     H           Henry's law constant
                                     BAF bioaccumulation factor
                                     BCF bioconcentration factor
                                     FCM food-chain multiplier
                                     soil IM        half-life in soil
                                     ksg         soil degradation rate
                                     D,          air diffusion coefficient
                                     vapor P      vapor pressure
                                     melting point in °C (needed only for the following compounds)
                                          benzo(a)pyrene              179 (e)
                                          benzo(h)fluoranthene          168 (e)
                                          heptachlor                   95.5 (b)
                                          hexachlorobenzene           231 (b)
                                     '     soil/water partition coefficient (Kd,) = Koc x fraction organic carbon in soil (OCpJ
                                          see Table 4)
                                          suspended sediment/water partition coefficient (Kd_,)  =  Koc x fraction organic
                                          carbon in suspended sediment (OC^, see Table 27)
                                     !  Fish BAF = BCF x FCM
Volume V
Appendix V-7
-------
Table 3
Chemical-specific Parameters for Inorganic Compounds
Compound
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium
(hexavalent)
Copper
Lead
Mercury ]
Nickel v
Selenium
Silver
RCF
L/kg
0 1 g
003 c
0008c
0015c
00015 c
0032c
00045c
O.I g
O.I g
0007c
0004c
002c
0 1 c
Bv'
0004 a
0 20 a
004 a
O.ISa
OOlOa
0 55 a
00075 a
0 40 a
0045 a
090a
0060 a
0025«
0 40 a
Br1
6 5 x 10' »
0030 a
0006«
OOI5a
OOOISa
0 I5a
0 0045 a
025 a
0.009 a
0.20 a
0060 a
0025 a
0 10 a
Ba beef
day/kg
00015 a
000! a
0002 a
1 5 x 10' a
0001 a
1 6 x 10' o
0 0055 a
OOlOa
3 0 x ia' a
8 0 x 10' o
0006 a
0 0030 o
0 003 a
Ba milk
day/kg
20 x 10' a
1 0 x \V a
6 0 x 10' a
3 5 x 10' a
90 x 10' a
1 0 x 10' o
0.0015 a
OOOISa
2 5 x 10' a
1 Ox Itf' o
0001 a
0 0045 o
0020 a
Ba pork
day/kg
0 28 g
0 007 e
0.0037 h
001 e
0002b
2 6 x 10' o
OOI5H
OOOSe
0.0018 b
0.0022 o
0.15b
028 o
9 0 x 10' e
Ba chicken
day /kg
792g
0.006 e
02011 b
5.0 x la' e
0.011 b
0.11 0
0.024 b
0002e
7.92 h
0031 o
0.024 b
1 17 o
9 0 x 10' e
Ba eggs
day/kg
792g
007 e
0.2615 b
04 e
0013b
0 0026 o
0039b
02 e
7.92 b
0 0026 o
0039b
1 17 o
0 0 1 8 e
Kd
L/kg or inl/g
1,500 a
45 a
200 a
60a
650 a
6 5 a
850 a
35 a
900 a
10 n
150 a
100 H
4S „
Fish BAF
L/kg
36d
1 c
44 c
4 m
20 c
2,213.1
I6c
290 h
I60d
4,994 i
85,700 i
61 k
78 1
0 5 c
Volume V
Appendix V-7
-------
                                                                                   Table 3
                                                             Chemical-specific Parameters for Inorganic Compounds
    Compound
RCF
L/kg
                                    Bv'
                             Br'
Ba beef
day/kg
Bn milk
day/kg
Ba pork
 day/kg
Ba chicken
  day/kg
Ba eggs
day/kg
    Kd
L/kg or ml/g
Fish BAF
  L/kg
   Thallium
                    00004c
                                 40x 10'a
                                               4 0 x  10' a
                                                                0.040 a
                                                                               0002 a
                                                                           0.28 g
                                                  7 92 g
                                                   7 92 g
                                                  l,500»
                                                                                                                                                                  120 c
   Zinc
0 1  g
                                    1 5 a
                                                 0 90a
                                                              I  2 x I04 o
                                                        3 Ox 10'o
                               1.8 x 10' o
                                                                                                                00091 o
                                                                                                                                 00091 o
                                                                                                                                                   40 a
                                                                                                  432 p
   NOTES
   ksg = 0 for all inorganic compounds (professional judgement)
   plant l,t  =  14 days for all compounds (n).
   1   The units for Bv and Br are (tng/kg plant DW|/|mg/lcg soil]
   2   Because mercury is assumed In exist as a vapor, the following additional parameters are
       required to evaluate its fate and transport (these parameters are assumed (o equal zero for all
       other inorganic compounds)
       air to leaf liiotransfer factor (Bv)  = 1000 |mg Mg/kg plant tissue DW|/(mg Hg/kg air) (c)
       air diffusion coefficient (Da) = 0 1423 cm'/sec (Lugg 1968)
       Vapor  Pressure = 0 002 mm Hg (0
   •   Baes el al   1984
   b   Belcher and Travis 1989
   c   US EPA I994b
   d   U.S EPA AQUIRE data base
   e   Baker el al. 1976
   f   U.S  EPA 1990H
   g   Because s literature value for this inorganic compound could not he located, the maximum
       value for this parameter for any inorganic compound on this  list is conservatively applied.
                                                                        h  U S. EPA 1985a.
                                                                        i   U.S  EPA I985H.  First value is for inorganic mercury, second value is for
                                                                           methylated mercury (midpoint of range of values).
                                                                        j   U S  EPA I985c
                                                                        k  U S  EPA 1980d
                                                                        I   U.S. EPA I980e
                                                                        m  The bioaccumulation factor (BAF) provided in (c) is assumed to apply
                                                                        n  US  EPA 1994a.
                                                                        o  U S  EPA 1995c.
                                                                        p  US  EPA 1980f
                                                                        RCF - root concentration factor
                                                                        Bv  - soil/plant transfer factor for vegetative crops (i.e., leafy vegetables)
                                                                        Br  - soil/plant transfer factor for nonvegetative (reproductive) crops
                                                                        Ba  - animal tissue biotransfer fauor
                                                                        Kd  - soil/water and suspended sediment/water distribution coefficient
                                                                        BAF - bioaccumulation factor
Volume V
Appendix  V-7
-------
Table 4
Site-specific Parameters |

oc!01,
BD
P
I
RO
Ev
0.
R
Parameter
Fraction of organic carbon in soil
(unitless)
Bulk density of soil (g/cm1)
Precipitation (cm/yr)
Irrigation (cm/yr)
Runoff (cm/yr)
Evapotranspiration (cm/yr)
Soil volumetric water content (mL/cm1)
LISLE erosi\ ily (yr ')
Value
0.013
1.31
95
28
25
44
0.25
125
Media
plant,
soil
soil
soil
soil
soil
soil
soil
soil
Basis 1
average of organic matter values provided in the Soil Conservation
Service soil surveys of Beaver & Lawrence (USDA SCS 1982),
Greene &. Washington (USDA SCS 1983), Butler (USDA SCS
1989), and Allegheny counties, PA (USDA SCS 1981); Brooke,
Hancock, & Ohio counties, WV (USDA SCS 1974); and
Columbiana county, OH (USDA SCS 1968) and assumption that II
the organic matter is comprised of 40-50% carbon (Foth and Turk
1972)
average of values provided in the Soil Conservation Service soil II
surveys of Beaver & Lawrence (USDA SCS 1982), Greene &
Washington (USDA SCS 1983), and Butler counties, PA (USDA
SCS 1989)
average of values provided in the Soil Conservation Service soil II
surveys of Beaver & Lawrence (USDA SCS 1982), Greene & 1
Washington (USDA SCS 1983), Butler (USDA SCS 1989), and
Allegheny counties, PA (USDA SCS 1981); Brooke, Hancock, &
Ohio counties, WV (USDA SCS 1974); and Columbiana county,
OH (USDA SCS 1968)
PA average (personal communication, Jarrett 1994)
PA average (personal communication, Jarrett 1994)
based on meteorological data from Columbus, OH (personal
communication, Reinke 1994)
regional average (personal communication, Seibert 1994)
constant for Allegheny county, PA (pcisonal commiiniciilion,
Mnyp.r IQ<>4» |
Volume V
Appendix V-7
-------
Table 4
Site-specific Parameters

K
u
T
/*.
P.
TP
YP
F
Aw
Parameter
USLE erodability (tons/acre)
Wind speed (m/sec)
Air temperature (K)
Viscosity of air (g/cm-sec)
Density of air (g/cm1)
Length of exposure to deposition per
harvest of the edible portion (yr)
Standing crop biomass (kg DW/rn2)
Fraction of feed from on-site sources
Effective watershed area (nr)
Value
0.34
4.1
293
1.82x 104
l.20x 101
0,226 ag exposed
0.288 leafy
0.315 forage
0.082 silage
0.09 ag exposed
0.1 8 leafy
0.449 forage
2.989 silage
0.9 for grain and
silage for dairy
cows, 1 .0 for all else
5.57 x 107 (TR L.)
1.3 x 109(LBC)
4 i 10' fOhin R )
Media
soil
soil
plant,
soil
soil
soil,
plant
plant
plant
animal
lake
river
Basis
average of values provided in the Soil Conservation Service soil
surveys of Beaver & Lawrence (USDA SCS 1982), Greene &
Washington (USDA SCS 1983), and Butler counties, PA (USDA
SCS 1989)
based on meteorological data from Pittsburgh, PA (personal
communication, Vreeland 1994)
average air temperature during summer months (USBC 1993)
calculated from the air temperature (Munson et al. 1990)
calculated from the air temperature (Munson et al. 1990)
time of harvesting activity (PDA 1994)
literature values for aboveground exposed and leafy vegetable
(Belcher and Travis 1989), average 1987 and 1992 grain, forage,
and silage values from Census of Agriculture (USI)C I993n,
1993b, 1993c)
personal communication, Miller 1993
CES 1994
USGS 1993
prnfpjiiinnfll jn/lppninnl
Volume V
Appendix V-7
10
-------
Table 4
Site-specific Parameters

A,.,
vw.,
TSS
PbR
Parameter
Surface area of water body (m2)
Volume of water (L/yr)
Total suspended solids (mg/L)
Particle emission rate (g/s)
Value
1.2x 10' (TR L.)
2.4 x 10' (LBC)
varies by subarea
(Ohio R.)
1.46x 10'°(TRL.)
4.7x 10" (LBC)
3.4 x 10" (Ohio R.)
I9(TR L.)
12 (LBC)
20 (Ohio R.)
0.07
0.07
Media
lake
river
lake
river
lake
river
lake
river
Basis
CES 1994
30 m avg width and 8,050 m length (professional judgement)
450 m avg width and lengths of 3.5, 3, 2, 2, 3, and 6.5 river miles
in the E3, E2, El, SI, W2, and W3 subareas, respectively
(professional judgement)
CES 1994
USGS 1993
personal communication, Fraser 1995
avg of bimonthly samples at three locations (CES 1994)
personal communication, Davic 1995
average of 1 0/89 to 6/92 monthly measurements from East
Liverpool Station, Ohio River (personal communication, Fraser
1995)
average of 35 runs from the trial burns and performance tests
ag exposed = above ground exposed fruit and vegetables
TR L. = Tomlinson Run Lake
LBC = Little Beaver Creek
Ohio R. = Ohio River
Volume V
Appendix V-7
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 1.   Estimation of Soil Concentrations
     It is assumed that a portion of each of the stack gas chemicals is deposited on surficial
 soils in the study area due to dry and wet deposition of panicles and  vapor.  The concentration
 of chemicals in surficial soil is required to estimate human exposure  to chemicals in soil
 through soil ingestion and dermal contact with soil, to predict uptake in vegetation for human
 consumption and grazing animals, and to estimate the concentration in  surface water.  Tables 5
 to 11  are used to estimate chemical concentrations in soil. Soil concentrations are estimated
 for surface (one centimeter) soils and root zone (20 centimeters) soil (U.S. EPA 1990a).  In
 addition, soil concentrations within the upper 10 centimeters are estimated as an input to
 estimating surface water concentrations (U.S. EPA 1994a), assuming an agricultural
 watershed, which could have some tilled and some untilled soils.  These soil concentrations are
 based on deposition rates of chemicals of concern assuming complete mixing within the soil
 layer of interest (surface, root zone, or average) and continuous operation of the facility over a
 period of 30 years.
     As presented in Table 5, various parameter values are needed to estimate soil
 concentrations.  Deposition rates and vapor-phase air concentrations used in the equation are
 determined from air dispersion modeling.  The deposition flux of vapor is estimated using the
 equation  in Table 6.  The soil loss constant (kse) is determined as the sum of four independent
processes: leaching, soil erosion,  surface runoff, and degradation (abiotic and biotic) (Table
 7).  Losses due to leaching (ksl), soil erosion (kse) and surface runoff (ksr) are estimated using
the equations presented in Tables 7, 8. and  10, respectively.  Losses due to degradation (ksg)
are empirical and are determined from a review of the literature. It is conservatively assumed
that additional losses due to volatilization do not occur because given all the opportunity for
volatilization to occur during atmospheric transport, once deposited, additional volatilization
losses from the soil are not expected.
Volume V
Appendix V-7                              1 ">
-------
TableS
Estimation of Soil Concentration (CS)1

Parameter
CS
Dvd
Dyw
*-THF
ks
Tc
Z
BD
100
cc (Dvtf - DVH- - 1^.) [l - * -^ ^>] (100)
(Z) (BD) (ks)
Definition
Chemical concentration in soil, me/kg
Drv deposition rate, g/nr-yr
Wet deposition rate, g/m:-yr
Atmospheric diffusion flux to soil, g/m:-yr
Soil loss constant, vr"1
Total time of deposition, yr
Soil depth, cm
Soil bulk density, g/cm3
Units conversion, (10"1 m:/cm2)(10- mg/g)dO' g/kg)
Value
Calculated value
Based on drv deposition model
Based on wet deposition model
See Table 6
See Table 7
30'
1 for soil contact"
10 for surface water*"
20 for plant uptake'
1.31C
100
Notes-
a - U.S EPA 1993
b - U.S EPA 1994a.
c - See Table 4.
Volume V
Appendix V-7
13
-------
Table 6
Estimation of Atmospheric Diffusion Flux to Soil (Ln(VV
LD,C = (0.31536) (Kt) (Cv)
Parameter
l~mc
Kt
cy
0.31536
Definition
Atmospheric diffusion flux to soil, g/nr-vr
Gas phase mass transfer coefficient, cm/s
Vapor-phase chemical concentration in air due to
direct emissions, /ig/m3
Units conversion,
CIO'2 m/cm)aO-6 g//ig)(3.1536 x 107 s/vr)
Value
Calculated value
See Table 1 1
Based on air dispersion model
0.31536
Notes.
a - U S EPA 1993
Volume V
Appendix V-7
14
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                                             Table?
                 Estimation of Soil Loss Constant (ks) and Soil Loss Due to Leaching (ksl)'
                                 ks  =  ksl +  kse + ksr +  ksg
                                                  - RO  -  Ev

Parameter
ks
ksl
kse
ksr
ks.e
P
I
RO
Ev
e
z
BD
Kd,
/6 \ C7) ] - (BD) 5
\vs) (.") l + \DLJ) Q
Definition
Soil loss constant, yr"1
Soil loss due to leaching, yr"1
Soil loss due to soil erosion, vr"'
Soil loss due to surface runoff, yr"1
Soil loss due to degradation, yr"1
Average ar^nal precipitation, cm/yr
Average annual irrigation, cm/vr
Average annual runoff, cm/yr
Average annual evapotranspiration, cm/yr
Soil volumetric water content. mLycm3
Soil depth of leaching, cm
Soil bulk density, g/cm3
Soil/water partition coefficient. mL/e
Value
Calculated value
Calculated value
See Table 8
See Table 10
Chemical-specific
95"
28b
25*
88h
0.25b
1. 10. or 20
1.31b
Chemical-specific
Notes
a - U.S. EPA 1993
h - See Table 4
Volume V
Appendix V-7
15
-------
Table 8
Soil Loss Due to Soil Erosion (Use)"

Parameter
kse
X,
BD
SDU
E
Z
Kd,
e.
0.1
^ _ for.) (SDJ(£) (0.1)1 F (&/,)<*/» 1
(BD)(Z) \[Qs + (Kds)(BD)\
Definition
Soil loss due to soil erosion, vr"'
Unit soil loss, kg/nr-yr
Soil bulk density, g/cm3
Sediment delivery ratio for watershed, unitless
Enrichment ratio, unitless
Watershed mixing zone depth, cm
Soil/water partition coefficient, mL/g or cnvVg
Soil volumetric water content, unitless or cnyVcm3
Units conversion. (m2/104 cnrHIO3 g/kg)
Value
Calculated value
See Table °
1.31h
See Table 30
3C
1. 10. or 20
Chemical-specific
0.25b
0.1
Moles
a - U.S EPA 1993
b - See Table 4
c - U.S EPA I994a
Volume V
Appendix V-7
Ifi
-------
Table 9
Unit Soil Loss (XJ'

V (R\ (JC\ (J  ( ton) ( 4.07x1 CT? Awj ^ w
Parameter
X.
R
K
LS
C
P.
Definition
Unit soil loss, kg/nr-yr
"Erosivity" factor, yr"1
"Erodabilitv" factor, tons/acre
"Topographic or slope length" factor, unitless
"Cover management" factor, unitless
"Supporting practice" factor, unitless
Value
Calculated value
125"
0.34"
0.179C
0.3d
1.0C
Notes
a - U.S. EPA 1990a.
b - See Table 4.
c - U.S EPA 1993
d - Default value for a rural setting (U.S. EPA 1994a)
Volume V
Appendix V-7
17
-------
Table 10
Soil Loss Due to Surface Runoff (ksr)1

Parameter
ksr
RO
e.
z
Kd.
BD
fr \ RO
J

1 ]


Definition
Soil loss due to surface runoff, yr"'
Average annual runoff cm/yr
Soil volumetric water content, unitless or cm3/cm3
Watershed mixing zone depth, cm
Soil/water partition coefficient, mL/g or cnrVg
Soil bulk density, g/cm3
Value
Calculated value
25"
0.25"
1. 10 or 20
Chemical-specific
1.31"
Notes
a - U.S EPA 1993.
b - See Table 4
Volume V
Appendix V-7
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                                          Table 11
                       Estimation of Gas Phase Mass Transfer Coefficient (KY

Parameter
K
u
srn
d.
M,
P,
D,
0 _ "„
"" PJP.)
Definition
Gas phase mass transfer coefficient, cm/s
Wind speed, m/s
Schmidt number for gas phase, unitless
Effective diameter of contaminated area, m
Viscosity of air. g/cm-sec
Air density, g/cm3
Diffusion coefficient of chemical in air. cm"/sec

Value
Calculated value
4.1*
Calculated value
200'
1.82x lO-4"
1.20x 10 3b
Chemical-specific
Notes
a - U.S EPA 1990a
h - See Table 4
Volume V
Appendix V-7
19
-------
2.   Estimation of Vegetation Concentrations
     The chemical concentration in vegetation is necessary to estimate human exposure to
chemicals through ingestion of vegetation (i.e., vegetables and fruit) as well as to estimate the
uptake of chemicals by animals that feed on the vegetation (i.e., grain,  forage, and silage).
Stack gas chemicals may bioaccumulate in plants through three mechanisms: uptake b\  roots.
direct deposition on exposed plant tissues, and air-to-plant transfer of vapor-phase chemicals.
These mechanisms are discussed more fully by U.S. EPA (1990a and 1994a).
     The magnitude of chemical uptake by vegetables is dependent on the type of vegetable
and its potential for exposure to the atmosphere. For example, contaminant deposition  onto
leafy vegetables is more likely to occur than onto vegetables that are protected from the
atmosphere, such as com or root vegetables.  Similarly, the uptake of chemicals from the soil
will differ for below ground and aboveground vegetables.  Therefore, four types of vegetable
classes are considered in the Human Health Risk Assessment: leafy vegetables (e.g., lettuce,
broccoli); aboveground protected vegetables (e.g., com, peas); aboveground exposed (e.g.,
tomatoes, green peppers); and root vegetables (e.g., carrots, onions). Assumptions for each of
these classes of vegetables are used in Tables  12 to 22 to estimate concentrations of chemicals
in vegetables.
     The total concentration of a chemical in  a given plant (CV) is due  to root uptake (Pr,),
direct deposition (Pdj), and air-to-plant  transfer (Pv,) as shown in Table 12.  Concentrations of
leafy, aboveground exposed and aboveground protected vegetables are calculated in dry
weight.  Because ingestion rates are based on  fresh weight, the dry weight vegetable
concentration is  converted to a wet weight concentration by multiplying by (1-water fraction),
as shown in Table  12. The concentration in root vegetables is calculated in  wet  weight  so a
similar conversion is not necessary.  Additionally, dry weight concentrations are needed for
grain, forage,  and silage precluding the need for a comparable conversion.
     Calculation of the total plant concentration is different for aboveground and below ground
vegetation and is described below.  As shown in Table 13, chemical concentration from root
uptake (Pr;) for aboveground vegetation (i.e..  aboveground exposed and protected vegetables,
and leafy vegetables) is dependent on the soil  concentration (CS) and a chemical-specific
plant/soil bioconcentration factor (Br,).   Baes  et al.  (1984) presents bioconcentration factors for
all the metals.  For organic chemicals, the bioconcentration factors are calculated using  an
equation developed by Travis and Arms (1988) and presented in Table 14.
     For below ground vegetation (i.e., root vegetables), Pr, is estimated by the method
                                                                   -f"
developed by Briggs (1982) and shown  in Table 15. Briggs (1982) developed a  regression
equation dependent on the octanol/water partition coefficient (Kow) to calculate root
Volume V
Appendix V-7
-------
 concentration factor (RCF,) values.  This equation is presented in Table 16. VGb? is a factor
 introduced into the calculation of contaminant concentrations to reflect the reduced
 translocation of compounds in bulky, below ground vegetables, such as carrots and potatoes
 (U.S. EPA 1994a).  In general, the contaminant concentrations measured in the barle\ roots of
 the Briggs (1982) experiments would be representative of the levels of compounds in the outer
 few millimeters of below ground vegetation, but much higher than the average concentration in
 the whole vegetable.  Thus, a VGbg value of 0.01 is used for all compounds (U.S. EPA
 1994b).
     The factors related to the plant concentration attributable to direct deposition on exposed
 plant tissues (Pd,) are presented in Table 17.  The site-specific parameters are presented in
 Table 17.  The wet and dry deposition rates are obtained from the air dispersion modeling.
 Fw is the fraction of wet deposition that adheres to plant surfaces and is assumed to equal 0.6
 for all organics and 0.46 for all metals, according to recommendations by U.S. EPA (1995c).
 Equations to calculate the interception fraction of the edible portion of plant tissue (Rp,) and
 the plant surface loss coefficient (kp) are presented in Tables 18 and 19, respectively.  Values
 of the length of a plant's exposure to deposition per harvest (Tp,) and  the yield or standing
 crop biomass (Yp,) are obtained from the PA Agricultural Statistics Service (PASS 1994) and
 the Census of Agriculture (USDC 1993a, 1993b, 1993c), respectively.  This route of exposure
 for plants is not  considered for aboveground protected vegetables and  root vegetables.
     Plant  concentrations attributable to air-to-plant transfer are dependent on the vapor-phase
 air concentration and an air-to-plant biotransfer factor, as can be seen  in Table 20. This type
 of transfer  applies only to aboveground  leafy and exposed plants (i.e., does not include root or
 aboveground protected vegetables).  The site-specific parameters are presented in Table 20.
 These factors are related to various physical and chemical properties of the chemicals.  Table
 21 presents equations used to estimate the air-to-plant biotransfer factor (Bv,).  The vapor-
 phase concentration due to direct emissions (Cy) is obtained from  the air dispersion modeling.
 VGag is a correction factor similar to VGb|. that is introduced to reflect the difference between
 the concentration in the outer few millimeters and the average  concentration in the whole
 vegetable.  Based on U.S. EPA's (1994a) recommendations, VG.g should be set equal to 0.01
 for unspecified aboveground fruits and vegetables,  1.0 for leafy vegetables and forage, 0.5 for
 silage, and 0 for grain. These recommendations are based,  in  part, on the reduction of
 chemical concentrations in unspecified fruits and vegetables as a result of cleaning and peeling;
the direct analogy of leafy vegetables and forage to azalea leaves, the experimental leaves on
                                                                   * *
 which the equation was based; the assumption that  silage can be considered part leafy and part
protected; and the assumption that grain is fully protected.
Volume V
Appendix V-7
-------
                                                     Table 12
                                     Estimation of Plant Concentration (CV)*
                                          CV   =   Pr  + Pd  ~ Pv
  for dry-to-wet weight conversion:

                         CV(wet weight);    =   \CV(dry weight)] (1  -  F water
    Parameter
                    Definition
           Value
       CV.'
Total chemical concentration in the ilh plant group,
mg/kg	
      Calculated value
        Pr,
Chemical concentration in i'h plant group due to
root uptake, mg/kg	
    See Tables 13 and 15
        Pd,
Chemical concentration in ilh plant group due to
direct deposition, mg/kg	
        See Table 17
        Pv,
Chemical concentration in
to-plant transfer, mg/kg
' plant group due to air-
        See Table 20
     Fwaier,
Water fraction in ilb plant group', unitless
         0.93 leafy'
 0.87 aboveground exposedd
0.78 aboveground protected"1
  Notes
   a -  U.S EPA 1990a
   b -  Uptake via direct deposition and air-to-plant transfer is assumed to be insignificant for aboveground protected and root vegetables   All
      three uptake pathways are assumed to be significant for aboveground exposed and leafy vegetables and gram, forage, and silage
   c -  Root vegetables are calculated in wet weight, and dry weight concentrations are needed for grain, forage, and silage so water fractions
      are not provided for these plant categories
   d -  Baes et'it  1984
Volume V
Aooendix V-7
-------
Table 13
Plant Chemical Concentration Due to Root Uptake in Aboveground Plants (Pr,)'
Pr, = (CS)(Br.)
Parameter
Pr,
CS
Brb
Definition
Chemical concentration in itb plant group due to root
uptake, mg chemical/kg plant tissue, dry weight fDW]
Soil chemical concentration after the total period of
deposition, me chemical/kg soil
Plant/soil bioconcentration factor for the i'h plant group,
(mg chemical/kg plant tissue DW]/[mg chemical/kg soil]
Value
Calculated value
See Table 5
Chemical-specific, see Baes et al.
(1984) for metals and Table 14 for
oreanics
Notes
a - U.S EPA 1990a
b - For uptake of metals bv aboveground leafv vegetables. Bv is used in Dlaoe of Br Values of Bv are listed in Bses el al (1984 1
Volume V
Appendix V-7
23
-------
Table 14
Plant/Soil Bioconcentration Factor for Organic Chemicals for Aboveground Plants (Br ,)"
LogBri = 1.588 - (0.578) (Lo^A^J
Parameter
Br,
K^
Definition
Plant/soil bioconcentration factor for organic
chemicals for aboveground plants, (mg
chemical/kg plant tissue DW]/[mg chemical/kg
soil]
Octanol/water partition coefficient, unitless
Value
Calculated value
Chemical-specific
Notes.
.-US EPA 1990s.
Volume V
Appendix V-7
-------
Table 15
Plant Chemical Concentration Due to Root Uptake in Below Ground Plants (Pr^l*

Parameter
(CS) (RCF) \VGt\
Pr ~ "
AW
Definition
Pr,^ Chemical concentration in ilb plant group due to root
uptake, me chemical/kg plant tissue, wet weight (WW)
CS Soil chemical concentration after the total period of
deposition, mg chemical/kg soil
RCF Root concentration factor, L soil water/ke plant tissue
VG^ Empirical
Kd, Soil/water
correction factor, unitless
partition coefficient. L soil water/kg soil

Value
Calculated value
See Table 5
See Table 16
0.01'
Chemical-specific
Notes-
a - L'.S EPA 1994b
Volume V
Appendix V-7
-------
Root Concentration Factor for
LogRCF
Parameter
RCF
Knu
Table 16
Organic Chemicals for Below Ground Plants (RCF)'
= (0.77) ILogKJl - 1.52
Definition
Root concentration factor for organic chemicals
for below ground plants, L soil water/kg plant
tissue, fresh weight
Octanol/water partition coefficient, unitless
Value
Calculated value
Chemical-specific
Notes:
a - U S EPA !994a
Volume V
Appendix V-7
-------
Table 17
Aboveground Plant Chemical Concentration Due to Direct Deposition (Pd,l*

Parameter
Pd,
1000
Dvd
Fw
Dvw
Rp,
kP
Tp,
Yp,
(1000) [Dyd * (Fw) (Dvw)] (/fc() 1 - e'(Kr>^r']
(^P,) (kp}
Definition
Chemical concentration due to direct deposition in the
ilb plant group, me chemical/kg plant tissue DW
Conversion factor. (10° kg/g)(106 me/kg)
Yearly dry deposition rate, g chemical/nr-yr
Fraction of wet deposition that adheres to plant
surfaces, unitless
Yearly wet deposition rate, g chemical/nr-vr
Interception fraction of the edible portion of plant
tissue for the i"1 plant group, unitless
Plant surface loss coefficient, vr'1
Length of plant's exposure to deposition per harvest of
the edible portion of the i" plant group, yr
Yield or standing crop biomass of the edible portion of
the ilh plant group, kg DW/nr
Value
Calculated value
1000
Based on drv deposition model
0.6 for oreanics"
0.46 for metals'
Based on wet deposition model
See Table 1 S
See Table 1°-
0.226 aboveground exposed"
0.288 leafs"
0.315 forage"
0.082 siiaee"
0.09 aboveground exposed"
0.18 leafy11
0.449 forage*1
2.989 silaee"
Notes
a - U S EPA 1993
b - See Table 4
c - U S EPA 1995c
Volume V
Appendix V-7
11
-------
Table 18
Interception Fraction for Aboveground Plants (Rp,)
Forage*:
Silage1":
Leafy Vegetables':
Exposed Vegetables':
Parameter
Rp,
YP
RP,
RP,
RP,
Rp's = 1 - e1^^
Rp" = i.e«"»>«»"
Definition
Interception fraction
for foraee. unitless
Standing crop biomass for ilh plant group, kg DW/nr
Interception fraction
Interception fraction
Interception fraction
for silaae. unitless
for leafv vegetables, unitless
for exposed produce, unitless
Value
Calculated value
See Table 1 7
Calculated value
Calculated value
Calculated value
Notes
a- U.S EPA 1990s
b - U.S EPA 1994a
c - Silage includes grains, leafy vegetables include brassica vegetables: exposed vegetables include legumes, fruiting vegetables and fruits
Potatoes and root vegetables are assumed to have interception fractions equal to zero
Volume V
Appendix V-7
-------
                                                 Table 19
                                    Plant-Surface Loss Coefficient (kp)'
                                      .        f In2 If  365da\'s\
                                      kp   =  \  	    	--
                                                t,,-,\  I     vr    )
                                                 '1/2
    Parameter
                  Definition
                                                                                  Value
        kp
Plant-surface loss coefficient, vrs"1
                                                                             Calculated value
                  Environmental half-time on plant surfaces, days
                                                          Chemical-specific
                                                     (assume 14 for all chemical?1^
   Notes
   a - U.S. EPA 1990s.
   b - U S EPA 1994a.
Volume V
Appendix V-7
-------
Aboveground Plant Chemical
Pvt
Parameter
J\
Cy
Bv,
VG,
P
10'
Table 20
Concentration Due to Air-to-Plant Transfer (Pv )'
(Cy) (ffv, ) (J'Gag)
(pj do3)
Definition
Chemical concentration due to air-to-plant transfer
in the ilk plant group, mg chemical/kg plant tissue
DW
Vapor-phase chemical concentration in air due to
direct emissions, ^g chemical/rrr air
Air-to-plant biotransfer factor for the i" plant
group, [mg chemical/kg plant tissue DW]/[mg
chemical/kg air]
Aboveground plant correction
factor, unitless
Density of air, ke/m'
Units conversion. me/lO~'we
Value
Calculated value
Based on air dispersion model
Calculated value, see Table 21
0.01 aboveground vegetable11
1.0 leafy'
1 .0 forage"
0.5 silage"
0 erain"
1.247 at 10 C
10'
Notes
a - L' S EPA 1994a
Volume V
Appendix V-7
-------
Table 21
Air-to-Plant Biotransfer Factors (Bv)*

Parameter
Bv
P
Bvo,
0.15
770
40
Br _ HOP-)
(0.15) (770) (40) ;
Definition
Air-to-leaf biotransfer, [me/kg DW]/|mg/kg air]
Density of air ke/m3
Bacci volumetric air-to-leaf biotransfer factor,
[mg/kg WW]/[ms/ke air]
Fraction of grass that is drv weight. 85%
Grass leaf density, g/L
Empirical correction factor
Value
Calculated value
1.247 at 10 C
See Table 22
0.15'
770'
40'
Notes
a - U S EPA 1994a
Volume V
Appendix V-7
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Table 22
Bacci Volumetric Air-to-Leaf Biotransfer Factors (BVJ"

Parameter
BVOI
Knu
H
R
T
/ H \
Ino R H C\f>S,\ l\r\o f,' \ - lr>o 1 fS^4
l°sDvoi H.UOD; (iogAoitj log i o?-+ ;
Definition
Bacci volumetric air-to-leaf biotransfer factor,
fmg/ke WW]/[mg/ke air]
Octanol/water partition coefficient, unitless
Henrv's constant. atm-nvVmole
Universal eas constant. atm-m3/mole-K
Temperature, K
Value
Calculated value
Chemical-specific
Chemical-specifu-
8.206 x 10"
293"
Notes
a - U S EPA 1993
h - See Table 4
Volume V
Appendix V-7
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 3.    Estimation of Chemical Concentrations in Meat, Eggs, and Milk
      Stack gas chemicals in soil and plants may accumulate in animals that ingest these media
 while grazing. The chemical concentration in animals is required to estimate human exposure
 to chemicals via consumption of meat products, eggs, and milk from livestock that have grazed
 on soils containing chemicals emitted from the stack. U.S. EPA (1993: 1994a) presents a food
 chain model to estimate concentrations of stack gas chemicals in beef. milk. pork, poultry.
 eggs, and deer meat.  This model considers the chemical concentration in plants and  soil, the
 quantity of plants and soil that animals consume, and the biotransfer (Ba) or bioconcentration
 (BCF) factor for each type of animal tissue.  Uptake of chemicals via inhalation and  ingestion
 of contaminated water is assumed to be insignificant and not considered in this assessment
 (U.S. EPA  1994a).
      Table 23 presents the algorithm used to estimate chemical concentrations in animal
 tissues. This equation includes uptake from ingestion of plants and  soil as well as a biotransfer
 or bioconcentration factor.  Estimation of the chemical concentration in plants was described
 previously.  Information in Table 24 provides additional input parameters of the type and
 amount of plants and soil consumed by various animals.
     Table 25 presents regression equations for non-dioxin-like organic chemicals that relate
 biotransfer factors to a chemical-specific octanol/water partition coefficient (Kow). It  should be
 noted, however, that the regression equations for beef and milk,  which were developed by
 Travis and Arms (1988), may contain residual error (personal communication, McKone 1995)
 and a recent study suggests that the biotransfer factor may be independent of Kov.  over a broad
 range (McLachlan 1994).
     Considerable scientific evidence exists to indicate that bis(2-ethylhexyl)phthalate is
 readily metabolized and  excreted, so that very little tissue accumulation occurs in mammalian
 species (Ikeda 1980; Daniel and Bran 1974; Astill 1989).  In rats, there is very little tissue
 accumulation following repeated dietary treatment with 14C-BEHP.  Significant uptake was
 found only in liver and fat,  and tissue half-lives for BEHP and its metabolites were estimated
 to be 3 to  5 days for fat and 1 to 2 days for other tissues (Daniel and Bratt  1974).  In
 cynomolgus monkeys, the rate of excretion of label was 50 to 80 percent in the first 24 hours.
 The average 24-hour excretion of label was lower in dogs (67 percent) and miniature  pigs (37
 percent) (Astill 1989). A comparative study of BEHP absorption and excretion in rats, dogs,
and pigs showed that the rate of clearance was rapid in all these species.  Less than 3  percent
of the administered dose was found to remain in the body tissues  after 96 hours ,  with most
remaining in the intestines,  and less thanl percent retained in muscle and fat (Ikeda 1980).
Volume V
Appendix V-7                             33
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     Metabolism of BEHP has been verified in several species including man (Schmid and
 Schlatter 1985).  These studies collectively indicate that there is very low potential for
 significant bioaccumulation of BEHP in the human food chain (ATSDR 1993a).  Based on the
 work of Dceda et al. (1980), a conservative "metabolism factor"  (MF) of 0.01 (to represent an
 upper limit of 1 percent remaining in fat and muscle) was used to modify the biotranster factor
 derived from Travis and Arms (1988) (see Table 23).
     An analogous MF (metabolism factor) was applied to di(n)octylphthalate (DNOP)
 because of the close similarity between DNOP and BEHP in chemical structure and
 metabolism (DeAngelo et al. 1986).  DNOP and BEHP are chemical isomers and. therefore.
 will behave comparably in the environment. Like BEHP, metabolism of DNOP  has been
 observed in several  species including man (Lake et al.  1977).  In fact. Kaneshima et al. (1978)
 reported that in rats, the metabolic rate of DNOP was faster than that of BEHP.   This
 observation results because the straight chain isomer, DNOP, has a simpler structure than the
 branched chain isomer, BEHP, so it is more susceptible to metabolism.  Quantitative data to
 calculate an MF for DNOP, however, were not available in this  study or other l"erature
 sources.  Because of DNOP's similarity to BEHP, an MF equivalent to that for BEHP was
 assigned to DNOP.  Based on the above, this assumption appears to be reasonably
 conservative.  Metabolism factors for all other compounds were conservatively assumed to be
 1.0.
     Egg concentrations are assumed to  be related to K^ by a regression equation developed
 by California EPA for their CalTOX exposure  model (CalEPA 1993).  The uncertainties
 associated witn  the use of these equations are discussed  more fully in the uncertainty section of
 the Human Health Risk Assessment.  These regression  equations are all based on  experimental
 data that relate the chemical concentration  in feed to the chemical concentration in animal
 tissue (fresh weight). For dioxin-like compounds (i.e..  conservatively includes chlorinated
 biphenyl compounds in addition to dioxin and furan compounds)  in beef, milk, pork, chicken,
 egg, and deer meat,  however, an empirical BCF is used that relates the concentration of the
 ingested feed to the concentration in animal fat. This BCF is congener-specific but is based on
 a study with one animal (U.S. EPA  1994a). The uncertainty section of the Human Health
 Risk Assessment discusses this uncertainty more fully.  The concentration in animal fat is
converted to fresh weight by multiplying by the fat fraction, as shown in Table 23.  For
 metals, biotransfer factors reported in the literature are used to estimate concentrations in
animal tissue (fresh weight).  Specifically,  biotransfer factors for cadmium, mercury,
 selenium, and zinc are presented in U.S. EPA (1995c).  For the other metals, the source of the
biotransfer factor is found in Table 3.
Volume V
Appendix V-7
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      To account for the fraction of the vegetation ingested by the animal that is grown near the
 farm site and thus could be impacted by incinerator emissions, an F, factor is introduced.  A
 value for F, is assigned based on local data on the fraction of grain, silage, etc. that is
 imported into the area.  Consumption of forage by the various livestock is assumed to have an
 F, of 1.0.  Consumption of grain and silage by the various livestock also has an F of 1.0 except
 for dairy cattle ingestion of grain and silage, which has an F, of 0.9.  These site-specific values
 were estimated based on a discussion with a local agricultural extension agent (persona!
 communication, Miller 1993).
      To correct for the differences in transfer efficiency of soil as compared to feed, a B,
 factor is added to the equation in Table 23. Because the BCF was developed based on
 vegetative intake, it must be reduced to account for the fact that soil is a less efficient vehicle
 of transfer as compared to feed.  A Bs of 0.65, therefore, is used as suggested by U.S. EPA
 (1994a).
     It should be noted that feed lot fattening  of beef cattle is not considered in this assessment
 because discussion with local agricultural agents indicated that no feed lots are present in this
 area.  If for some reason, however, beef cattle are fattened prior to slaughter (e.g., a farmer
 has a special diet for his cattle or beef cattle are sent to feed lots outside the area and return to
 the area as beef), the concentration in beef could be overestimated by about a factor of two.
 This overestimation  does not apply for the  subsistence farmer scenario,  however,  because it is
 reasonable to assume that feed lot fattening does not occur (U.S. EPA 1994a).
     Chicken and  egg concentrations may be similarly overestimated if  chickens are raised in
 cages because the equations to estimate chicken concentrations are based on free-ranging
 chickens. Caged chickens would not have access to contaminated soil like free-ranging
 chickens, so their soil intake  would be reduced.  However, because soil  intake is assumed to
 make up only 3% of a chicken's total intake, this overestimation is likely to be small.
Volume V
Appendix V-7
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Table 23
Estimation of Chemical Concentration in Animal Tissues (CBl'
CB - ±(QPlJ) (CF) (FJ - (Qs; ) (CS) (B*;) (A/F)
[1=1 J
or for dioxin-like compounds'5:
r -i
C» ^ ±(DFpv}(CVv)fv)^(DF^(CS}^(BCF)\fatj}
l'=i J
Parameter
CB
Op,, °r
DFPl)
CV,
F,
Qs or DFs
CS
B,
BSi
MF
BCF
fat
Definition
Chemical concentration in the jlk animal tissue group, mg
chemical/kg animal tissue fresh weight
Quantity of the i'b plant tissue eaten by the jtk animal each
day or fraction of diet that is the i'b plant tissue, kg plant
tissue DW/dav or unitless
Total chemical concentration in the ilk plant group eaten
by the jlh animal, mg chemical/kg plant tissue DW
Additional adjustment factor to account for grain or silage
that is imported from outside areas, unitless
Quantity of soil eaten by the jlb animal each day or
fraction of diet that is soil, kg soil/day or unitless
Soil concentration, mg chemical/kg soil
Soil bioavailabilitv term, unitless
Biotransfer factor for the j" animal tissue grc ^p, d/kg
Metabolism factor, unitless
Bioconcentration ratio of contaminant, unitless
Fraction of j"1 animal tissue that is fat. unitless
Value
Calculated value
See Table 24
See Table 12
0.9 for dairy cattle grain and silage
1 .0 for all elsec
See Table 24
See Table 5 0 cm depth)
0.65b
Chemical-specific, see Baes et al.
(1984) for metals and Table 25 for
oreanics
Chemical-specific
(0.01 for BEHP and 1.0 for all
other chemicals)
Congener-specific
See Table 25
a - modified from U.S EPA 1993
h - U S EPA 1994a
^ - See Table 4
Volume V
Anoendix V-7
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Table 24
Feed and Soil Consumption Rates for Various Animals
Animal
Beef cattle
grain
forage
silaee
Dairy cow
grain
forage
silaee
Hogs
grain
silaee
Chickens (grain)
Deer (forage)
Quantity of Plants Consumed by Animals
(Qp,,). kg DW/day
12'
0.47" (4 %=)
8.8' (72%")
2.5' (21 %=)
17'
2.6' (15%°)
11' (64%=)
3.3' (19%"]
4.3'
3.0' (65%=)
1.3' (28%=)
0.08' (97%=)
1.6" (99%=)
Quantity of Soil Consumed b\ Animals
(QSi). kg/da\
0.26" (2 %••>
0.33' (2%r>
0.34b (7£=)
0.0024" (3 %=)
0.0185e(19f=1
Notes
a - U.S EPA 1990s
b - U.S EPA 1993
c- Percent of diet (DF X 100%)
d - Dee 1991
e - Arthur and Aldredge 1979 as cited in Clement 1989
Volume V
Appendix V-7
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                                          Table 25
               Biotransfer Factors fBaj) for Non-dioxin-like Compounds and Fat Fractions
    \ozBa(beef)  =   -76
                                                              (a)
                          lozBa(milk)  =   -8.1  + logAovi      (a)
                         r>  /    7\      f T~)  /1.   ./\ 1 I    po^K \      f i \
                         Ba(pork)  =   [Ba(beef)\  	       (o)
                                                    '6ee/y
Ba (chicken)   =  [Ba(beef)}
                                                   -
                                                                 (V)
                         lozBa(eggs)  =   -5.1  - log A'       (c)
Parameter
8a
K»
fat..
fatm,..
fat^,,
foU^r
fat,..
fet^,.
Definition
Biotransfer factor, d/ke
Octanol/water partition coefficient, unitless
Fraction of beef that is fat. unitless
Fraction of milk that is fat. unitless
Fraction of pork that is fat. unitless
Fraction of chicken that is fat. unitless
Fraction of egg that is fat, unitless
Fraction of deer meat that is fat. unitless
Value
Calculated value
Chemical-specific
0.23d
0.02'
0.23d
0.058d
0.08C
0.04d
a - U.S EPA 1990a
b - Professional ludgement
c - CalEPA 1993
d - Pennmgion 1989
e - USDA 1994
Volume V
Aonendix V-7
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 4.   Estimation of Surface Water Concentration
      Surface water bodies may receive stack gas chemicals from direct deposition, from runoff
 of contaminated soils in the vicinity of the WIT facility, and from eroded soils.  The chemical
 concentration in surface water is required to estimate human exposure through surface water
 ingestion and dermal contact, and to estimate the uptake of chemicals from the surface water
 by fish. U.S. EPA  (1994a) presents a model to estimate chemical concentrations in surface
 water bodies, shown in Tables 26 to 33.  This model, and not other models suggested by U.S.
 EPA (e.g., U.S. EPA 1990a; 1993) is used because it was developed specifically for dioxin-
 like compounds, the class of chemicals that present the greatest health effects in this
 assessment.  Additionally, this model contains fewer uncertain parameters than the other
 models. The assumptions contained in this algorithm include the following:

      •   The impact to the water body is correlated to concentrations on watershed soils and
          particles that deposit on the water body,
      •   Soil concentrations within a watershed and impacts to the water body are uniform,
      •   Sorption of compounds onto surface soil,  suspended solids, and bottom sediments is
          principally a function of the contaminant's organic carbon partition coefficient (K^)
          and the organic carbon content of soils and sediment,
      •   Chemicals enter into a surface water body via soil erosion,  surface runoff,  and
          direct deposition,
      •   The concentration of contaminants on eroding soil is "enriched" due to the
          preferential erosion of lighter and higher organic matter material and the preferential
          binding of contaminants to these lighter and higher organic matter material,
     •   The concentration of contaminants sorbed  to suspended matter is "enriched"
          compared  to bottom sediments for similar reasons, that is, contaminants will
         .preferentially bind  to panicles that remain in suspension because they tend to be
          lighter and have higher organic matter material as compared to particles that settle to
          the bottom,
     •    Steady state is achieved between the concentration in the dissolved phase in the
          water  column, the concentration in the suspended sediment, and the concentration in
          bottom sediments,
     •    A mass balance  is maintained between the soil reaching the water body via  erosion
          and direct  deposition, the suspended sediment, and the bottom sediment,  and
     •    Volatilization out of and degradation in the water body are not modeled,  nor is
          resuspension of bottom sediment.
Volume V
Aorjendix V-7
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     To determine surface water concentrations, the concentration on the suspended sediment
must be estimated. The suspended sediment concentration is calculated with the total  load of
chemical to the water body (p) and the annual amount of suspended sediment (4>). as presented
in Table 28. The values for p and  are determined by the equations in Tables 29 to 33.
     Once the suspended sediment concentration is determined, the dissolved concentration is.
estimated by calculating a mass balance between the mass of contaminants entering the water
body and the amount that partitions to the three compartments in the water body, a) dissolved
in the water column, b) sorbed to suspended material, and c) sorbed to particles settling to the
bottom. Specifically, the dissolved concentration is estimated by assuming that equilibrium is
maintained between the sorbed and dissolved phases (Table 26). The bottom sediment
concentration is determined by the relationship with the concentration on the suspended
sediment shown in Table 27. This relationship assumes that suspended  sediment
concentrations are enriched in comparison to bottom sediment concentrations, according to the
organic carbon content.
Volume V
Appendix V-7
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Table 26
Estimation of Surface Water Concentration (CVVT

Parameter
CW
c_
Kc^
c
/-ff' _ ssed

Definition
Dissolved-phase concentration in water column,
me/L
Concentration on suspended sediment, mfi/ke
Suspended sediment/ water partition coefficient for
contaminant in suspended sediment, L/kg

Value
Calculated value
See Table 28
Chemical-specific
Notes
a - U.S EPA 1994a
Volume V
Appendix V-7
41
-------
Table 27
Concentration on Sediment (C_H)*

Parameter
c.,.
c_
oc^
oc^
- - ic \ °H
"- sec/ \"~ ssedl /I/"1 1
> Lued)
Definition
Concentration on sediment, mg/ke
Concentration on suspended sediment, me/ke
Fraction organic carbon in bottom sediment,
unitless
Fraction organic carbon in suspended sediment,
unitless
VaJue
i
Calculated value
See Table 28
0.03'
0.05'
Notes
a - U S HP*, 1994a
Volume V
Appendix V-7
-------
Table 28
Concentration on Suspended Sediment (C_J*
i
c = £
"ed 
Parameter
C~-
P
*
Definition
Concentration on suspended sediment, me/kg
Annual contaminant entry via erosion + direct
deposition, m.e/vr
Annual amount of suspended sediment, kg/yr
Value
Calculated value
1
See Table 29
See Table 32
Notes:
a - U.S EPA I994a
Volume V
Appendix V-7
-------
Table 29
Annual Contaminant Entry via Erosion -t- Direct Deposition (pi"
p = (CSvb) (E/g - Z>£P.
OS;, = (OS-) (£)
1
Parameter
P

cs^
ER,
DEPC

CS

E
xr
A,
SD,
Definition
Annual contaminant entrv via erosion 4- deposition.
me'vr
Concentration on soil entenne water body, me'ke
Total watershed erosion, ke/vr
Annual deposition of contaminant on water bod\ .
me/vr
Average soil concentration in effective area of
watershed, mg/kg
Enrichment ratio, unitless
Unit soil loss, kg/m'-vr
Effective drainage area of watershed, rrr
Sediment deliverv ratio for watershed, unitless.
Value
Calculated value

Calculated value
Calculated value
See Table 3 1

See Table 5

3'
See Table &
See Table 4
See Table 30
Notes
a - 1! S EPA 1994a
Volume V
Appendix V-7
A A
-------
                                                Table 30
                               Sediment Delivery Ratio for Watershed (SD,)'
                                                           -0.125
Parameter
SDU
a
A.
Definition
Sediment delivery ratio for watershed, unitless
Empirical intercept coefficient, unitless
Effective drainage area of watershed. m:
Value
Calculated value
See below
See Table 4
Notes
a - U.S EPA 1993
                 Watershed Area
                  (square miles)
                      < 0.1
                       1
                       10
                      100
                      1000
"a" Coefficient

     2.1
     1.9
     1.4
     1.2
     0.6
Volume V
Appendix V-7
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Table 31
Annual Deposition of Contaminant on Water Body (DEP.T
DEPC = (Dyd - Dyu-) (4uw) (1000)
Parameter
DEPC
Dyd
Dyw
A,,
1000
Definition
Annual deposition of contaminant on water body,
mg/yr
Dry deposition rate, g/nr-yr
Wet deposition rate, g/m~-yr
Surface area of water body, m2
Units conversion. 10' mg/g
Value
Calculated value
Based on dry deposition model
Based on wet deposition model
See Table 4
1000
Notes
a - U.S EPA 1994a
Volume V
Appendix V-7
-------
Table 32
Annual Amount of Suspended Sediment (<£)"
V OC
. _ wot ,*<. ,pp \ + if \ inrp \ + se* r/1 f\ IFP \ + n f \ /DFP v
Kd ™ ' w> **> ' w or t' /J> ^ ^ ( •/*/) (DEPP)I
^ssed U<~ss*l
Parameter
0
v«
Kd^
f,
ER.
f-
DEPP
oc...
oc,^
Definition
Annual amount of suspended sediment, kg/yr
Water body annual volume, L/yr
Suspended sediment/water partition coefficient,
L/kg
Fraction of annual erosion remaining as suspended
materials, unitless
Total watershed erosion, kg/yr
Fraction of ann""l deposition remaining as
suspended materials, unitless
Total annual direct deposition of particles, kg/yr
Fraction organic carbon in bottom sediment,
unitless
Fraction organic carbon in suspended sediment,
unitless
Value
Calculated value
See Table 4
Chemical-specific
See Table 33
See Table 29
1.0*
See Table 33
0.03'
0.05"
Notes
a - U S EPA 1994a. -
Volume V
Appendix V-7
47
-------
Table 33
Fraction of Annual Erosion Remaining as Suspended Materials (f,) and
Total Annual Direct Deposition of Particles (DEPJ*

Parameter
f,
TSS
v«
ER,
DEPP
PER
RDEPP
A«
10-6
io-3
(7SS) (>U (10-*)
E*»
DEPp = (PER) (RDEPp) (A^)
Definition
Fraction of annual erosion remaining as suspended
materials, unit less
Total suspended solids. mg/L
Water body annual volume. Uyr
Total watershed erosion, kg/yr
Total annual direct deposition of particles, kg/yr
Particle emission rate, g/s
Rate of particle deposition, g/nf-yr
Area of water body, m~
Units conversion, 10"6 kg/mg
Units conversion, 10"3kg/g
(io-3)
Value
Calculated value
(not to exceed 1.0)
See Table 4
See Table 4
See Table 29
Calculated value
0.07"
Based on dry + wet deposition
model
See Table 4
10*
io-3
Notes
a - U S EPA 1994t
b - SeeTible4.
Volume V
Appendix V-7
48
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 5.    Estimation of Chemical Concentrations in Fish
      Stack emissions may enter local surface water bodies through both direct deposition and
 deposition onto watershed soils followed by runoff and erosion into the surface water bodies.
 Once in the water body, these stack gas chemicals may be incorporated into fish.  The
 chemical concentration in fish is required to estimate human exposure to chemicals via
 ingestion of fish. U.S. EPA (1990a) presents a model to estimate chemical concentrations in
 fish.  This model, which calculates chemical concentrations by considering the water
 concentration and a bioconcentration factor (BCF), is generally appropriate for chemicals  with
 high  water solubility and low affinity for sediments.  This equation relates the concentration of
 chemicals in the fish to the dissolved concentration in water but does not consider uptake from
 other sources such as diet.  The equation was modified,  therefore, to include a
 bioaccumulation factor (BAF) instead of a BCF.  Bioaccumulation refers to uptake of a
 chemical from all sources such as diet and bottom sediments as well as the ambient water.
 This  equation is presented in Table 34.  Estimation of water concentrations were described
 previously.  BAFs are calculated as the product of a  BCF and a food-chain multiplier (FCM)
 (U.S. EPA 1995b).  U.S. EPA (1995b) presents FCMs for various trophic levels based  on log
 Kow. The FCMs for the piscivorous fish trophic level 4 are used in this assessment.  BCF
 values for specific substances of concern are compiled from the scientific literature and other
 sources, e.g., the U.S. EPA AQUIRE data base.
      It  should be noted that the BCF for mercury differs depending on its form (e.g.. methyl
 mercury' or inorganic mercury) in the water column,  with methyl mercury incorporated by fish
 nearly ten times as much as inorganic mercury.  The rate of methylation in the water column is
 affected by microbial action  and abiotic processes and generally results in no  more than 25 %
 of the total mercury in a water column existing as a methyl mercury complex. In reality, less
 than 10% is typically observed (U.S. EPA  1994c). This assessment, however, conservatively
 assumes that 25% of the total mercury in the water column exists as a methyl mercury
 complex.  Additionally, it should be noted  that the accumulation of PAHs in fish is
 conservatively evaluated in this assessment. Despite  their high lipid solubility, these
 compounds are readily metabolized (ATSDR 1993b,  Eisler 1987), so significant
 bioaccumulation is not expected.  This conclusion is further substantiated by West et al.  (1984)
 who observed that higher molecular weight PAHs, which include the largest class of chemical
 carcinogens and those selected as surrogate organic chemicals in this assessment, do not appear
to accumulate in fish.  However,  for the purposes of  this assessment,  PAHs are assumed to not
 metabolize in fish, and they are evaluated in the same manner as the other chemicals.
Volume V
Appendix V-7                             49
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     Because dioxin-like compounds have a low water solubility and high affinity to
sediments, U.S. EPA (1994a) suggests an alternative equation, which is also provided in Table
34.  Estimation of bottom  sediment concentrations (Csed) was described previously. The biota
to sediment accumulation factor (BSAF) is a congener-specific value that relates the chemical
concentration in the organic carbon of the bottom sediment to the concentration in the lipid of
the fish.  It is an empirical value derived from the literature. The lipid concentration is
convened to a whole fish concentration by multiplying by the fraction lipid content of fish
(fllpld), assumed to be 0.07  (U.S. EPA 1994a).
Volume V
Appendix V-7                             50
-------
Table 34
Estimation of Chemical Concentration in Fish (CF)'
1
CF = (CW) (BAF)
or for dioxin-like chemicals'":
( c \
rrr _ 1 sed 1 IB
-------
6.   Estimation of Chemicals in Mothers' Milk
     Constituents in breast milk provide an exposure pathway to infants, a potentially sensitive
population sub-group.  Travis et al.  (1988) presents a generic methodology to estimate breast
milk concentrations of organic compounds.  This methodology is summarized in Table 35.
The mothers' total daily intake is summarized in Table 36. Biotransfer factors are a function
of the octanol/water partition coefficient (Kow) and can be calculated by the modified  Travis et
al.  (1988) equation shown in Table 37. As noted in  Section 3 of this appendix, a metabolism
factor, MF, is applied to account for the metabolism of bis(2-ethylhexyl)phthalate in
mammals.  Based on studies on the metabolism of bis(2-ethylhexyl)phthalate in the human
food chain (Tkeda et al. 1980; Daniel and Bratt 1974), a metabolism factor of 0.01 is applied
for this compound.  For all other compounds, the value of MF is 1.0 (i.e.,  no metabolism is
assumed to occur).  Inorganic compounds, including metals, are not generally lipophilic and
thus accumulation in mother's milk is not anticipated.
     Smith (1987) developed an alternative approach to estimating concentrations in breast
milk for dioxin-like compounds.  This approach is based  on the half-life of dioxins within the
human body, estimated as five to seven years (U.S. EPA 1994a), and can be seen in
Table 35.
     The lifetime average  maternal intake relevant to the infant's exposure is the mother's
average daily dose during her lifetime, rather than the dose during the period of exposure.
The LT over ED factor is added to correct for the lifetime averaging of maternal intake (i.e.,
to estimate an average daily dose during the period of exposure) as represented in Table 36.
Volume V
Appendix V-7                              52
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Table 35
Concentrations in Mothers' Milk (C^J"

( JT
r - IKA \ ic \ 1 L1
"-mm r'li) P mm) 1 r-n
or for dioxin-like compounds6:
(») w ft) &) (

Parameter
Cmir
M,,
F_,
MF
m
h
f
f.
f.
LT/ED
(MF)
LT\
(0 693) (/•.,) ( ED)
Definition
Chemical concentration in mothers' milk, me/kg
Maternal total daily intake from all routes of
exposure, me/day
Mothers' milk biotransfer factor, day /kg
Metabolism factor, unitless
Lifetime average maternal intake of dioxin-like
compound, me/ke of bodv weight/da\
Half-life of dioxin in adults, days
Proportion of ingested compound stored in fat
Proportion of mother's weight that is fat. kg
maternal fat/ke total bodv weight
Fraction of lipid content in breast milk
Lifetime over exposure duration, unitless
Value
Calculated value
See Table 36
See Table 37
Chemical-specific
(0.01 for bis(2-athylhexyl)phthalate and
1.0 for all other chemicals)
M,/70 kg, See Table 36
2555 assumed for all dioxin-like
compounds"
0.0'
0.3'
0.04C
Population-specific
Notes
a - U S EPA 1993
h - U.S. EPA 1994a
c - Smith 1987
Volume V
Appendix V-7
53
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Table 36
Maternal Total Daily Intake (M,,)
H, = Ms + MS, + Mp+Ma~ Mf + Masr
Parameter
M,,
M,
Msu
MP
Ma
M,
Mu,
Definition
Maternal total daily intake from all routes of
exposure, mg/dav
Maternal total daily intake from exposure to soil,
me/day
Maternal total daily intake from exposure to
surface water, mg/dav
Maternal total daily intake from exposure to
ingestion of plants, mg/dav
Maternal total daily intake from exposure to
ingestion of animals, mg/dav
Maternal total daily intake from exposure to
ineestion offish, ma/dav
Maternal total daily intake from exposure to air.
me/dav
Value
Calculated value
Calculated value"
Calculated value'
Calculated value'
Calculated value*
Calculated value"
Calculated value"
Notes
a - Thi1- value is estimated bv multiplying the appropnate estimated concentration bv the exposure assumptions
Volume V
Appendix V-7
54
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                                                  Table 37
                                 Organic Chemical Biotransfer Factors (Fmn,)*
                                      F
    Parameter
Definition
                                                                                    Value
                  Mothers' milk biotransfer factor, dav/ke
                                          Calculated value
                  Octanol/water partition coefficient, unitless
                                         Chemical-specific
                  Fraction of lipid content in breast milk
                                               0.04"
   Note
   a - modified from U.S. EPA 1993.
   h - Smith 1987
Volume V
Appendix V-7
               55
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TABLE 38
Key Assumptions in Fate and Transport Modeling
Assumption
Fate and transport modeling accurately reflects reality
Chemical-specific inputs are appropriate
Site-specific inputs are appropriate
I he surrounding area in nn agricultural watershed thai has
a soil mixing lone of 10 cm
The chemicals mix completely within the soil layer of
interest (1, 10, or 20 cm)
The facility operates continuously for 30 years
Volatilization losses do not occur once the chemical is
deposited
Degradation of organic contaminants in soil is first-order
Fruits and vegetables are modeled as four types of
vegetable classes
Hxposure to contaminants for aboveground protected
vegetables and root vegetables occurs only through root
uptake (i.e . does not occur via direct deposition and air-
to-plant transfer)
Basis
The U.S. HPA-recommended (U.S. FPA 1990a, 1993,
I994a) models used in this assessment are based on the best
available data (although somewhat limited). To account for
potenital uncertainty associated with the use of these data,
conservative assumptions are generally applied in developing
these models.
Professional judgment on best available data.
Professional judgment on best available data.
U S. F.PA (I994a) guidance assuming an agricultural
watershed has some tilled and some unfilled soils.
U.S RPA (I990a) guidance assuming tilling in agricultural
lands.
Conservative assumption although it is highly unlikely that
the facility will operate 100% of the time for 30 years. The
facility only operated 53% of the time in the first year.
Conservative assumption based on professional judgment.
Simplifying assumption to explain a complex process that is
not necessarily first-order.
U.S. F.PA (I990a and 1993) guidance.
U.S. RPA (199()a) guidance based on the likelihood (hal these
classes of vegetation are not exposed to contaminants on
depositing particles or in vapor form.
Magnitude
of Effect
high
high
low
low
low
low
low
low
low
low
Direction of
Effect
likely
overestimate
likely
overestimate
unknown
overestimate
overestimate
likely
overestimate
overestimate
overestimate
unknown
possible
underestimate
Volume V
Appendix V-7
56
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TABLE 38
Key Assumptions in Fate and Transport Modeling
Assumption
Uptake transfer factors for root uptake and air-to-leaf
uptake are based on Knu, '
Inhalation and surface water ingestion by animals are not
evaluated
Meat biotransfer (Ba) and bioconcentration (BCF) factors
are appropriate
All chlorinated biphenyl compounds are considered to be
transported in (lie same manner as the dioxin and furan
congeners
For surface water:
-Soil concentrations within a watershed are uniform
-Steady-state is achieved between concentrations in the
dissolved phase, suspended sediment, and bottom sediment
Of the total mercury in the water column, 25% exists in
the methyl mercury form
PAHs are evaluated as if no metabolism occurs in fish
Basis
U.S. EPA (1990a, 1993) guidance.
These pathways are considered insignificant compared to
fodder and soil ingestion (U.S. EPA 1994a) based on a
review of the literature.
U.S. F.PA (199(!a and I994a) guidance and review of
available models.
Conservative assumption based on professional judgment.
U.S. EPA (!994a) guidance.
U.S. EPA (1994c) guidance that concludes that no more than
25% of the total mercury in the water column exists in the
methyl mercury form and typically, less than 10% is
observed.
Conservative assumption since the literature (ATSDR I993b;
Eisler 1987) suggests that PAHs are readily metabolized in
fish.
Magnitude
of Effect
medium
low
high
low
low
low
low
Direction of
Effect
unknown
underestimate
unknown
underestimate
unknown
overestimate
possible
overestimate
Volume V
Appendix V-7
57
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                                                                    TABLE 38
                                                  Key Assumptions in Fate and Transport Modeling
                       Assumption
                                                                 Basis
Magnitude
 of Effect
 Direction of
   Effect
  Inorganic compounds do not accumulate in mother's milk
                                        Inorganic compounds are generally not lipophilic and would
                                        not tend to accumulate in mother's milk.
   low
underestimate
  Moles
  low
  medium
  high
less than a factor of two
a factor of two to ten
greater than a factor of ten
Volume V
Appendix V-7
                                                      58
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 McLachlan, M.S.  1994.  Model of the fate of hydrophobic contaminants in cows. Environ.
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     conversation.  June.

 Montgomery, J.H., and Welkom. L.M.   1990.  Groundwater chemicals desk reference.
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 Moyer, R.. Allegheny County, PA, Soil Conservation Service.  1994.  Telephone
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 Munson, B.R.,  D.F. Young, T.H Okiishi. 1990.  Fundamentals of fluid mechanics.   Toronto,
     Canada: John Wiley & Sons.

 Pennington, J.A.T.  1989.  Food values of portions commonly used. 15th ed.  New York:
     Harper and Row.

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Appendix V-7                            61
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Pennsylvania Department of Agricultural (PDA).  1994. 1993 - 1994 statistical summary arid
     Pennsylvania Department of Agriculture annual report.  Pennsylvania Agricultural
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Reinke, B., Midwest Regional Climate Center.  1994. Telephone conversation. November
     11.

Schmid. P. and C. Schlatter.  1985. Excretion and metabolism of di(2-ethylhexyl)phthalte  in
     man. Xenobiotica  15: 251-256.

Seibert, D.,  Soil scientist for southwest Pennsylvania. 1994.  Telephone conversation.
     October 28.

Smith, A.H. 1987.  Infant exposure assessment for breast milk dioxins and furans derived
     from waste incineration emissions. Risk Analysis 7(3):347-353.

Travis, C.C., and A.D. Arms.  1988.  Bioconcentration of organics in beef, milk, and
     vegetation. Environ. Sci. Technol.  22(3):271-274.

Travis, C.C., H.A. Hattemer-Frey,  and A.D. Arms.  1988.  Relationship between dietary
     intake of organic chemicals and their concentrations in human adipose tissue and breast
     milk.  Arch. Environ.  Contam. Toxicol.  17:473-478.

U.S. Department of Agriculture (USDA).   1994.  Federal milk order market statistics: 1993
     annual summary.  Statistical Bulletin No. 886.  August.

U.S. Department of Agriculture Soil Conservation Service (USDA SCS). 1968.  Soil survey
     of Columbiana County, Ohio.

U.S. Department of Agriculture Soil Conservation Service (USDA SCS). 1974.  Soil survey
     of Brooke, Hancock, and Ohio Counties, West Virginia.

U.S. Department of Agriculture Soil Conservation Sen-ice (USDA SCS). 1981.  Soil survey
     of Allegheny County,  Pennsylvania.

U.S. Department of Agriculture Soil Conservation Service (USDA SCS). 1982.  Soil survey
     of Beaver and Lawrence Counties, Pennsylvania.

U.S. Department of Agriculture Soil Conservation Service (USDA SCS). 1983.  Soil survey
     of Greene and Washington Counties. Pennsylvania.

U.S. Department of Agriculture Soil Conservation Service (USDA SCS),. 1989.  Soil survey
     of Butler County, Pennsylvania.
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Appendix V-7                             62
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 U.S. Bureau of the Census (USBC). 1993. Statistical abstract of the United States: 1993.
      (113th edition.)  Washington, D.C.

 U.S. Department of Commerce (USDC).  1993a.  1992 Census of Agriculture. Volume I.
      Geographic Area Series, Pan 35,  Ohio, State and County Data. AC92-A-35.

 U.S. Department of Commerce (USDC).  1993b.  1992 Census of Agriculture, Volume 1.
      Geographic Area Series, Pan 38,  Pennsylvania, State and County Data. AC92-A-38.

 U.S. Department of Commerce (USDC).  1993c.  1992 Census of Agriculture,  Volume 1.
      Geographic Area Series, Pan 48,  West Virginia, State and County Data. AC92-A-48.

 U.S. Environmental Protection Agency (U.S. EPA).  1980a. Ambient water quality criteria
     for phthalate esters.  Office of Water Regulations  and Standards, Washington. D.C.
      EPA/440/5-80/067.

 U.S. Environmental Protection Agency (U.S. EPA).  1980b. Ambient water quality criteria
     for carbon tetrachloride. Office of Water Regulations and Standards, Washington.  D.C.
      EPA/440/5-80/026.

 U.S. Environmental Protection Agency (U.S. EPA).  1980c.  Ambient water quality criteria
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 U.S. Environmental Protection Agency  (U.S. EPA).  1980d.  Ambient water quality criteria
     for nickel. Office of Water Regulations and Standards, Washington. D.C.  EPA/440/5-
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 U.S. Environmental Protection Agency  (U.S. EPA).  1980e.  Ambient water quality criteria
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 U.S.  Environmental Protection Agency  (U.S. EPA). 1980f.  Ambient water quality criteria
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 U.S. Environmental Protection Agency  (U.S. EPA). 1983.  Environmental transport and
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U.S. Environmental Protection Agency (U.S. EPA).  1985b.  Ambient water quality criteria
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U.S. Environmental Protection Agency (U.S. EPA).  1990a.  Methodology for assessing
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Appendix V-7                             64
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Appendix V-7                            65
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                           APPENDIX V-8



                      Estimation of Exposure Factors
Volume V
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A.     Introduction
       This appendix identifies the typical and high-end exposure factor values thai are used
in estimating dose in the risk assessment (Chapter VII) and conducting the sensiti\ it\  analysis
(Chapter VIE) for the WTI hazardous waste incinerator.  In this appendix, typical refers to
values that represent the mean or median of the distribution of possible values.  As noted in
the Exposure Assessment Guidelines  (U.S. EPA 1992a), for skewed or truncated
distributions, the median may be more representative of the central tendency value than the
mean. Most exposure factor distributions are skewed or truncated; therefore, when possible.
the median value is used. The term  "high end" refers to the values toward the upper end of
the distribution,  generally 90th percentile and greater.
       As discussed in Volume U, the key assumptions that are used in performing the risk
assessment have been identified.  Table 34 at the  end of this appendix summarizes the key
assumptions that are used in developing exposure factors.  The table of key  assumptions
indicates the basis for the assumptions listed, the  estimated relative magnitude of effect each
assumption is estimated to have on the overall risk assessment, and the direction of the
effect, if known.  It is  not anticipated that any of the assumptions made in estimating
exposure factors would have a significant (high1)  effect on overall results.

B.     Exposure Factors
       This appendix summarizes the values and the sources of these values for exposure
factors specific to the exposure pathways.  A number of exposure factors, however, are not
expected to change .between exposure pathways, such as exposure duration, body weight, and
averaging time.  Exposure duration is based  on the estimated length of time that an individual
resides at one location.  For adult residential  exposure, U.S. EPA (1990a) recommends
typical (50th percentile) and high-end (90th percentile) values of 9 and  30  years,
respectively, based on U.S. census data.  For both the typical  and high-end exposure
duration estimates for children, exposure duration is  assumed to be six  years (corresponding
to the assumed age range of the child, 1 to 6 years).  The subgroup of school-age children is
assumed  to have an exposure duration of six years for both the typical and high-end exposure
duration estimates, corresponding to  the typical period of school for an elementary school
child.  For the exposed farming subgroup, U.S. EPA (1990a)  recommends "typical" and
"worst case" exposure  durations of 20 and 40 years,  respectively.  These values are used as
    1 A "high" effect is estimated to be equal to a potential over- or underestimate of total
risks by a factor of ten or more.

Volume V
Appendix V-8                               i
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typical and high-end exposure durations, respectively, for adult farmers and subsistence
farmers.  These exposure durations are presented in the tables of exposure factor values
provided later in this appendix.
       Body weight is a second exposure factor that is specific to each exposure group but
does not  change from one exposure pathway to another. The adult exposure subgroups (i.e..
resident,  farmer, and subsistence farmer) are assumed to have a body weight of 70 kilograms
(typical and high-end). The child resident exposure subgroup is assumed to be pre-school
age children (i.e.,  1 to 6 years-old).  Based on U.S. EPA (1990a) guidance, the average
body weight for a  child in this age range is approximately 15 kg (average of male and female
children).  For the school-age children, who are  assumed to be in the age range of 7 to 12
years, a body weight of 31 kg is assumed, based on data presented by U.S. EPA (1990a).
       In an exposure assessment,  it  is generally necessary  to provide two different estimates
of the exposure dose (for each pathway), one for substances with noncancer effects, which is
referred to as the average daily dose  (ADD), and a second for substances with carcinogenic
effects, referred to as the lifetime average daily dose (LADD).  The ADD is the dose that an
individual is likely to receive on any  day during  the period  of exposure.   In cases where the
exposure is intermittent, it is generally appropriate to average the dose over the period of
exposure; therefore, the averaging  time is  equal to the exposure duration  in units of days
(ED in years x 365 days/year). For  carcinogens, the LADD is estimated by averaging the
total cumulative dose received by an  individual over a lifetime, which is estimated by U.S.
EPA (1989) to be 70 years (25.550 days).
       All other remaining exposure  factors vary based on the exposure group and  the route
of exposure.  The values used to determine doses for each of the routes of exposure are
discussed below for ihe remaining  factors.

       1.     Inhalation of Ambient Air
             Direct exposure to chemicals released from the WTI facility stack may occur
       to individuals living in the vicinity of the  facility.  The  following factors must be
       considered when estimating exposure via this pathway:  1) the concentration  of
       chemical in the air;  2) the inhalation rate; and 3) the frequency and duration of
       exposure.  Values of the exposure factors for this pathway are presented in Tables 1
       and 2.
             U.S. EPA (1990a) recommends an adult inhalation rate of  20 nWday (0.833
       m3/hr).  This value is used  for the typical and high-end inhalation  rate  for all adult
                                                                 /••
       subgroups.  For school-age children, an inhalation rate  of 20 nvVday (0.833 m3/hr) is
       also used for the typical and high-end values based on age-specific inhalation rates
       compiled by U.S. EPA (1990a).  For children  in all other subgroups (not including

Volume V
Appendix V-8                              n
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       school-age children), a value of 16 mj/day (0.667 m3/hr) is estimated, based  on age-
       specific inhalation rate data presented by U.S. EPA (1990a).  This value is used for
       both the typical and high-end values.

       2.      Soil Ingestion
              Exposure to chemicals in soil is assumed to occur through  incidental ingestion
       of soil by adult and child residents,  farmers (including subsistence farmers), and
       school-age children.  The following factors must be considered when estimating
       exposure via this pathway: 1) the chemical concentration in soil: 2) the rate of soil
       ingestion; and  3) the period of time over which  ingestion occurs.  The exposure
       factors for this pathway are provided in Tables 3 and 4.  The values used for the
       period of exposure,  body weight, and averaging time were discussed earlier.  The
       remaining factors are the soil ingestion rate, and the exposure frequency.

              a.     Soil Ingestion Rate
                    The soil ingestion rates used in the WTI Risk Assessment are based on
              various sources of U.S. EPA guidance.  Very limited data  are available to
              estimate the incidental ingestion of soil by adults.  A value of 25 mg/day for
              an "average adult" is cited by U.S.  EPA (1990b), based on work performed by
              LaGoy  (1987).  This value is used for the typical soil ingestion rate for  adult
              residents. U.S. EPA (1991) recommends a value of 100 mg/day for
              individuals older than six years of age as an "upper bound" value.  This value
              is used  as the high-end estimate  of soil ingestion for adult residents.
                    For children under six years, U.S. EPA (1990b) recommends a high-
              end value of between 100 and 200 mg/day for ingestion of  soil.  The lower
              and upper ends of this range are used as  the typical and high-end ingestion
              rates for children, respectively.
                    The soil ingestion rate for school-age children is based on soil  ingestion
              data presented by U.S. EPA (I990a).  Soil ingestion rates divided between
              indoor (3 mg/day) and outdoor (50 mg/day) are presented by U.S.  EPA
              (1990a), based on a study by Hawley (1985).  These values are prorated based
              on the assumption that indoor exposure would occur year round  (365
              days/year) and outdoor exposure would only occur during warmer months
              (estimated to be 200 days/year, based on the number of days that the
                                                               j^
              maximum daily temperature exceeds 50 P). The resulting  typical ingestion
              rate for school-age children  is estimated to be  30 mg/day.
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                    For the high-end ingestion rate for school-age children, the same
              method is used, but it is assumed that the outdoor soil ingestion rate is  100
              mg/day (for 200 days/year).  The indoor soil ingestion rate is still assumed to
              be 3 mg/day.  The resulting prorated high-end soil ingestion  rate is estimated
              to be approximately 60 mg/day.
                    The soil ingestion rates for farmers are based on U.S. EPA (1991)
              guidance for outdoor workers and residential ingestion rates.   It is assumed
              that farmers would ingest significantly greater amounts of soil during periods
              of outdoor field work.  For the high-end ingestion rate, a value of 480
              mg/day, recommended by U.S. EPA (1991) for outdoor workers, is  applied to
              farmers working in the field.  The typical soil ingestion rate  for farmers
              working in the field is assumed to be 100 mg/day, an upper-bound estimate for
              typical residential  exposure (U.S. EPA 1991). During non-field activities, it  is
              assumed that farmers would have the same soil ingestion rates as adult
              residents. 25 mg/day and  100 mg/day for the typical and high-end values.
              respectively.
                    It should be noted that the above estimates  of soil ingestion are assumed
              to incorporate consumption of household dust.  U.S. EPA (1991) guidance
              indicates that its estimates of 200 mg/day for 1 to  6 year-old  children and 100
              mg/day for other age groups are upper-bound values that account for ingestion
              of both outdoor soil and indoor dust.  In addition,  as indicated above, soil
              ingestion rates for school-age children are estimated based on "outdoor" and
              "indoor" (i.e., dust) exposure.  It should also be noted that in this assessment
              it is assumed that the concentration  of contaminants are equal in outdoor soil
              and indoor dust.
                    It is likely that household dust originates from one or  more of the
              following sources: 1) airborne paniculate matter that is transported from
              outside air to inside air; 2) surface soil and outdoor dust that  is tracked  into
              homes and buildings; and  3)  indoor dust generated by material degradation,
              use of household products, and other activities.

              b.     Exposure Frequency
                    An exposure frequency for soil ingestion  of 350 days/year
              recommended by U.S. EPA (1991)  is used for the typical and high-end
              estimate for all exposure subgroups.  This assumes that incidental soil
              ingestion occurs both indoors and outside.
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                     For the farmer, the exposure frequency is divided between outdoor
              field work and non-field work.  Site-specific data are not available: therefore.
              a reasonable period of exposure is estimated.  It is assumed that exposure
              frequency is divided equally between field and non-field activities.

       3.     Dermal Contact with Soil
              Dermal exposure to chemicals in soil in the vicinity of the facility may occur
       when residents (children and adults), school-age children, and farmers come into
       contact with soils. The following factors must be taken into account when evaluating
       this potential route of exposure: 1) the chemical concentration in soil; 2) the skin
       surface area exposed to the soil;  3) the amount of soil deposited on the skin: 4) the
       frequency and duration of exposure; and 5) the extent to which  chemicals adsorbed to
       the soil are subsequently absorbed through the skin.  The exposure factors for this
       pathway are presented in Tables 5 and 6.  Those not discussed previously are
       presented below.

              a.      Skin Area Exposed
                     The amount of skin available for exposure to soil is estimated  based on
              the expected activities and  types of clothing worn during the exposure period.
              For the typical value of skin area exposed, it is assumed  for all exposure
              subgroups that on average, exposure would primarily occur to hands and
              forearms.  Age-specific skin surface areas of these body  parts derived from
              U.S. EPA (1990a) guidance are  summed to estimate the typical values.
                  .   For the high-end value, it is assumed that the area of exposure is the
              hands,  forearms, and half the head  and legs.  Age-specific skin surface area
              values compiled by U.S. EPA (1990a) for these body parts are added  to
              estimate high-end values.

              b.      Soil to Skin Adherence Factor
                    The amount of soil  that adheres to the skin affects the amount of
              chemical that is available for absorption through the skin. U.S. EPA  (1992b)
              recommends a  typical value of 0.2 mg/cm2 and a high-end value of  1.0
              mg/cnr.

              c.     Absorption Factor
                    Limited data are available to estimate chemical-specific absorption
              factors  for the constituents  being considered in the risk assessment.  For
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             2.3.7.8-TCDD, U.S. EPA (19925) recommends a range of 0.001 to 0.03 (0.1
             to 3 percent) for the dermal absorption fraction.  Data for other dioxin-like
             compounds are not available; therefore, the upper end of this range. 0.03. Ls
             used as the dermal absorption fraction for all dioxins. furans. and dioxin-like
             compounds considered in the risk assessment.  For other organic compounds.
             a value of 0.06 (6 percent) is used, based on the upper end of the range of
             values (0.006 to 0.06) estimated by U.S. EPA (1992b) for trichlorobenzene.
             Similarly, for metals, a value of 0.01 (1 percent) is used, based on  the range
             of absorption fractions (0.001 to 0.01)  estimated by U.S. EPA  (1992b) for
             cadmium.

             d.     Exposure Frequency
                    It is assumed that dermal contact with soil would occur  at the same
             frequency as  soil ingestion.  Therefore, the exposure frequencies for dermal
             contact with soil for all subgroups are assumed to  be the same  as the exposure
             frequencies for soil ingestion.
                    As noted earlier, the period of exposure for farmers is divided between
             outdoor field work and non-field activities for farmers.  It is  assumed that
             exposure frequency is divided equally between field and  non-field activities.

       4.     Consumption of Meat and Eggs from Locally Raised Livestock
             Exposure to contaminated  meat  and eggs may occur when residents and local
       farmers consume meat (beef, pork, and poultry) from livestock raised  in the vicinity
       of the facility. The extent of exposure to chemicals through this pathway  is
       dependent on: 1) the chemical concentration in the meat or eggs; 2)  the meat or egg
       ingestion rate; 3) the fraction of meat or eggs ingested that comes from a local
       source; and 4) the frequency and  duration  of exposure.  Exposure factors used in this
       pathway are presented  in Table 7  and 8 and are discussed below.

             a.      Consumption Rate
                    Age-specific consumption rates for meats (including beef, pork, and
             poultry) and eggs are estimated  based on a 1987-88 national food consumption
             survey performed by the U.S. Department of Agriculture (USDA 1993a).  For
             children, median food consumption rates are estimated based on a weighted
                                                                r*
             average of food consumption rates for 1 to 2-year-old and 3 to  5-year-old
             children (based  on the percentage of the survey population in each group).
             Food consumption rates for school-age  children are based on weighted
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               averages for 6 to 11-year-old girls and 6 to 11-year-old boys.  Adult food
               consumption rates are based on the weighted average of adult  (older than 20
               years) males and females.
                     USDA (1993a) reports consumption data in several categories of meat
               products (e.g., lunch  meats, sausages, etc.); therefore, consumption rates of
               specific meats (e.g., beef, pork, chicken) were developed from a combination
               of data for several food types.  Specifically, age-specific meat  consumption
               data are presented by USDA (1993a) in several categories including: (1) beef,
               (2) pork, (3) lamb/veal/game,  (4) organ meats, (5) frankfurters/sausages/lunch
               meats, (6) chicken, (7) other poultry, (8) fish/shellfish, and (9) meat mixtures.
               Consumption rates of lamb/veal/game (3 listed above) and organ meats (4) are
               relatively insignificant and are not considered further in this analysis.  Meat
               consumption included in the frankfurters/sausages/lunch meat category (5) is
              proportionally divided between the beef (1), pork (2), chicken  (6). and other
              poultry categories (7), based on the consumption rate data for these individual
              meat types reported by USDA (1993a).  Similarly,  the meat mixtures category
              (9)  is divided proportionally between the beef (1), pork (2), chicken (6), other
              poultry (7),  and fish/shellfish (8) categories.  The resulting meat consumption
              estimates are summarized in Table 9.
                     High-end meat consumption rates are not available from the USDA
              (1993a) data. Therefore, high-end consumption rates are estimated by the
              product of median consumption rates presented in Table 9 and  the ratio of 90th
              percentile to median of individual food consumption rates estimated from
              consumption rate distributions developed by Pao et al. (USDA  1982).  The
              90th percentile to median ratios for the foods in Table 9 are presented in Table
              10.  Estimated high-end  meat consumption rates are presented in Table 9.

              b.      Exposure Frequency
                     The USDA consumption data are based on daily consumption;
              therefore, the exposure frequency is  assumed to be 350 days per year as
              recommended by U.S. EPA (1991).

              c.     Fraction Ingested from Contaminated Source
                    Although no data are available that directly measure the  fraction of
              meat consumption in the area of the WTI facility that is derived from locally
              raised livestock, statistics concerning the raising, marketing, and slaughter of
              livestock in the region  surrounding the WTI facility  are available.  The
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              following description provides a summary of the cattle-raising data that are
              available and the methodology used to estimate the fraction of beef consumed
              that is from locally raised cattle.   A similar process is used for the other types
              of meat  commodities.
                    The primary source of information on beef farming statistics is
              agricultural data compiled by the Agricultural Statistics Service associated  with
              the Departments of Agriculture in each of the three  states (Ohio. Pennsylvania.
              West Virginia) located in the vicinity of WTI (ODA 1994: PDA 19Q4: WVDA
              1994).  Summaries of livestock data are published annually and include such
              parameters as the total number of cattle/calves in the state and the number of
              calves bom annually. Table 11 summarizes state-wide beef farming statistics
              for Ohio, Pennsylvania,  and  West Virginia. The value for total cattle/calves in
              Table 11 is the number of cattle related to beef and  dairy farming that were
              reported in the state as of January 1,  1993.  In addition, the number of calves
              born in each state annually is provided in Table 11.
                    Information on the disposition of beef cattle and calves is also provided
              in the Agricultural Statistics  Service summaries.  The number of cattle and
              calves that are slaughtered  in registered slaughtering facilities in each state is
              shown in Table 11.  The source of the slaughtered animals, however, is not
              available because processing  facilities are not required to keep records on the
              origin/owner of the cattle sold for slaughter.  A report on the state of the
              slaughtering industry in Ohio (Distad  1992) indicates that Ohio does not have
              any  "large" capacity cattle  slaughtering facilities, but does have many smaller
              operations with slaughtering  capacities of less than 1,000 head per year.
              Furthermore, the report  indicates that Ohio is a net exporter of beef for
              slaughter.  Based on slaughter data published by the West Virginia Department
              of Agriculture (1994), the same situation would appear to hold  true for West
              Virginia.
                    Pennsylvania, on  the other hand, is home  to two of the largest cattle
              slaughtering facilities in  the country (10th and 12th largest overall) with a total
              annual slaughtering capacity  of approximately  740,000 head (Distad  1992), of
              which a  large fraction are likely to be imported from out of state. Because of
              these two very large plants (both  of which are located in the eastern part of the
              state), Pennsylvania is a  net importer of beef cattle for slaughter.  For the
                                                                 /•
              present analysis, it  is necessary to estimate the number of cattle that are raised
              in Pennsylvania and are  slaughtered in Pennsylvania. Including the data from
              these plants would significantly overestimate this  value.  To obtain an estimate
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              of Pennsylvania-bred cattle slaughtered in the state,  therefore, the 740.000
              head slaughtered at the large slaughtering houses in  eastern Pennsylvania are
              subtracted from the state total slaughter. The resulting estimate. 22°.000
              head, is more consistent with the other states in the  area and with the 220.000
              beef steers raised in the state (PDA  1994).  This value, therefore, is used to
              estimate the number of Pennsylvania-bred cattle slaughtered in the state.
                     County-specific beef farming data available from the Agricultural
              Statistics Service data summaries are limited.  It is necessary, therefore, to
              estimate a number of parameters based on state-wide data.  Published data
              (ODA 1994; PDA 1994; WVDA 1994) on the total  cattle herd in each of the
              three counties (Columbiana,  Ohio; Beaver, Pennsylvania; and Hancock, West
              Virginia) that are included in the risk assessment study area are provided in
              Table 12.  In addition, the calf crop in each of these three counties, and the
              cattle and  calf slaughter are  estimated  based on the fraction of the state herd in
              each county and the state-wide statistics in Table 12.
                     This methodology assumes that beef raising and slaughter practices are
              similar across all pans of a state, which may not necessarily be true.  To
              address this uncertainty, agricultural extension agents for the counties located
              in the vicinity of the WTI facility were interviewed regarding local beef cattle
              raising practices. Although  no actual data were obtained from these sources.
              judgments concerning local farming practices proved to be a valuable resource
              to supplement the state-wide  data.
                     For example, the primary type  of beef farming performed in the eastern
              Ohio/western Pennsylvania area involves cow/calf operations that raise cows to
              produce calves.  These calves are raised locally for 6 to 9 months, weaned,
              and generally sold to feedlots out of state (personal communication,  county
              agricultural extension agents. August  1994).  In other portions of these  states
              (Ohio, Pennsylvania, West Virginia), this practice may not be as
              commonplace.
                     The state-wide statistics,  therefore, may not accurately represent local
              beef farming practices.  For example,  according to the state-wide data (ODA
              1994; PDA  1994; WVDA 1994), the fraction of calves born that are marketed
              ranges from 0.23 for Ohio to 0.51 for West Virginia.  Discussions with local
              agricultural extension agents  indicate, however, that  60 to 70 percent of a  local
              calf crop in  any given year is marketed (sold at auction to feedlots in western
              Ohio or the  western U.S.) and may range as high as 80 to 90 percent of the
              local calf crop, but  is rarely  below 50  percent.  It is  likely, therefore, that
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              estimates of local slaughter provided in Table 12 overestimate actual local
              slaughter in these counties.
                     Based on the limited data available, the following methodology is used
              to estimate the availability of locally raised beef in the vicinity of the WTI
              facility:

              •      Beef slaughter in counties included within the study area is estimated
                     based on state-wide cattle slaughter data, as presented in Table 13.

              •      It is assumed that beef cattle slaughtered within the three-count) area is
                     consumed within the same area.

              •      The amount of beef derived from each head of slaughtered cattle is
                     estimated to be 50 percent of the average live weight of cattle
                     slaughtered in the state (1,100 pounds for  Ohio,  1,200 pounds : -.r
                     Pennsylvania, and 1,000 pounds for West  Virginia per: ODA 1994;
                     PDA 1994; WVDA 1994).

              •      The amount of beef derived from  calf slaughter is estimated similarly
                     based on average live weights for calves of 500 pounds in Ohio and
                     400 pounds in Pennsylvania (ODA 1994; PDA 1994).  West Virginia
                     calves are assumed to have an average live weight of 450 pounds.

                     Table 13 provides an estimate of locally raised beef available for
              consumption within each county in study  area.  Based on age-specific
              population within the three-county area (CACI 1992), presented in Table 14,
              and age-specific beef consumption rates (Table 9), the total annual beef
              consumption in the three-county area is 19.8 million pounds.  Therefore.
              locally  raised beef accounts for approximately 15  percent.  It  is likely  that this
              methodology overestimates the fraction of beef consumed that is raised locally,
              based on the type of beef raising performed in the area surrounding WTI.
                     For other types of meat products (i.e., pork,  chicken,  turkey) and eggs,
              a similar analysis of available livestock-raising statistics  was conducted. For
              pork, the number of hogs slaughtered in each of the three counties is estimated
                                                                   *'"*
              based on the product of the fraction of the total state hog herd in each county
              and the total state hog slaughter.  Assuming one-half of  a hogs live-weight is
              used for consumption, the total pork available for consumption is estimated as

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               1.53 million pounds, as shown in Table 15.  Based on the age-specific
               population within the three-county area (14) and age-specific pork consumption
               rates (Table 9), the total annual pork consumption in the three-county area is
               8.63 million pounds.  Therefore, pork from locally raised livestock accounts
               for approximately 15 percent of the pork diet for residents in the vicimu of
               WTI.
                     For chickens, agricultural census data (USDC 1993a,b.c) indicate that
               very few chicken farms (for meat) are located in the three counties located
               within the study area.   According to the agricultural census data,  the total
               number of broilers within the three-county area was less than 400 birds in
               1992. It is estimated, therefore, that locally raised chicken would comprise an
               insignificant portion of a typical resident's diet.  A similar conclusion was
               developed for turkey.
                     The fraction  of egg diet for residents that is derived from locally raised
               chickens is estimated based on the number of eggs produced locally and the
               local population.  Table 15  summarizes the egg data for the three counties
               surrounding the WTI facility and presents the estimated amount of eggs from
               locally raised chickens.   Total egg consumption in the three-county area
               surrounding the WTI facility is approximately 20.6 million pounds.  Based on
               the age-specific population (Table  14) and age-specific egg consumption rates
               (Table 9),  the total annual egg  consumption in the three-county area
               surrounding the WTI facility is approximately 5.5 million pounds.  Therefore.
              locally raised eggs account for  approximately 16 percent of the egg diet for
              local residents.
                     The high-end values  for the fraction of meat (or eggs) consumed by
              residents that is from locally raised livestock are estimated to be two times the
              average values.
                     For farm families, limited data are available to estimate the fraction of
              meat and eggs that are derived  from  locally raised livestock.  The  fraction of
              meat and eggs consumed that is  local is estimated based on information
              provided by U.S.  EPA (1990a) for consumption of beef by farm families.  The
              estimated central tendency and high-end values, therefore, are estimated to be
              0.44 and 0.75,  respectively, as  indicated in Table 7 and 8.
                    It is also assumed that a subgroup of farmers may exist that derive all
              tneir meat from their own farm (subsistence  farmers)/ A value of  1 (i.e., 100
              percent) is applied for this exposure subgroup of subsistence farmers.
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       5.     Consumption of Milk and Milk Products from Locally Raised Cows
             Exposure to contaminated milk and milk products may occur when residents
       and local farmers consume milk and milk products from cows that have been raised in
       the vicinity of the facility.  The extent of exposure to chemicals through this pathu a\
       is dependent on: 1) the chemical concentration in the milk and milk products: 2)  the
       consumption rate of milk and milk products; 3) the fraction of milk and milk products
       ingested that comes from a local source; and 4) the frequency and duration of
       exposure.  Exposure factors used in this pathway are presented in Tables  16  and  17
       and are discussed in the following sections.

             a.     Milk and Milk Products Consumption Rate
                    Age-specific consumption rates for milk and milk products are
             estimated based on a 1987-88 national food consumption survey performed b\
             the U.S. Department of Agriculture (USDA 1993a).  For children,  median
             food consumption rates are estimated based on a weighted average of
             consumption rates for 1  to 2-year-old and 3 to 5-year-old children (based on
             the percentage of the survey population in each group). Consumption rates  for
             school-age children are based on weighted averages for 6  to 11-year-old girls
             and 6 to 11-year-old boys.  Adult consumption rates are based on the weighted
             average of adult (older than 20 years) males and females.
                    USDA (1993a) reports  milk and dairy products consumption data in
             several categories including: (1) total milk products, (2) milk and milk drinks
             (subdivided into (2a) fluid milk and (2b) yogurt), (3) milk desserts,  and (4)
             cheese.   Consumption rates for cheese (category 4), milk desserts (3).  and
             yogurt (2b) listed by USDA (1993a) are used and are presented in Table 18.
             The consumption rate of "milk and milk drinks" listed in Table 18 is the total
             milk and milk drinks (category 2) consumption rate reported by USDA (1993a)
             minus the yogurt (2b) consumption rate. The cream consumption rate in Table
             18 is estimated by subtracting the identified categories (i.e., milk and  milk
             drinks  [2], milk desserts  [3], and cheese [4]) from the total milk products
             consumption rate reported by USDA (1993a).  The resulting consumption  rates
             for the various age groups considered in the risk assessment are summarized in
             Table 18.
                    It should also be noted  that  the butter consumption rate shown in Table
             18 is based on the consumption rate for "table fats" reported by USDA
             (1993a). Because the table fats category listed by USDA  includes margarine
             and butter substitutes, it is likely that the butter consumption rate in Table 18
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              is overstated; however, the butter consumption rate is relatively low and will
              likely not have a significant effect on food consumption risks.
                     High-end milk and milk product consumption rates are estimated as
              described earlier for beef.  The upper end of the consumption distribution is
              estimated as the product of median consumption rates presented in Table  1 8
              and the ratio of 90th percentile to mediaii of individual food consumption rates
              estimated from consumption rate distributions developed by Pao et al. (USDA
              1982). The 90th percentile to median ratios for the foods in Table 18 are
              presented in Table 10.  Estimated high-end milk and milk product consumption
              rates are  presented in Table 18.

              b.      Exposure Frequency
                     The USDA consumption data are based on daily consumption:
              therefore, the exposure frequency is assumed to be 350 days per year as
              recommended by U.S. EPA (1991).

              c.      Fraction Ingested from Contaminated Source
                     Table 19 summarizes the available milk cow, production, and
              marketing data available from the Agricultural Statistics Services for Ohio,
              Pennsylvania, and West Virginia (ODA 1994; PDA 1994; WVDA  1994).
                     Agricultural extension  agents representing counties in the vicinity of the
              WTI facility were contacted to provide a local characterization of dairy
              farming practices (personal communicatijon. county agricultural extension
              agents, August 1994).  In general, the extension agents reported that dairy
              farming in the  eastern  Ohio/western Pennsylvania area is  not significantly
              different from other parts of Ohio and Pennsylvania, and  that state-wide
              statistics are likely  applicable.  Table 20 provides estimates of county-specific
              milk cow herd  size and milk production statistics, and estimates of milk
              marketing, based on the state-wide data for the three counties surrounding the
              WTI facility.  The  milk marketing data include information on milk marketing
              to plants/dealers and direct  sales to consumers.  Discussions  with the
              agricultural extension agents indicate that the milk marketing to plants and
              dealers is divided between large processing  facilities that are not generally
              located in the area and smaller, local processing facilities that generally service
              communities within 5 to 10 miles of the processing facility.
                    To estimate the distribution of milk between the large processing
              facilities and the local handlers, a USDA (1988) milk marketing report that
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              summarizes county-by-county and state contributions to federally inspected
              milk processing plants (these are the large processing facilities referred to
              above) was reviewed. Federally inspected milk processing plants are assigned
              to "milk marketing areas" under the Federal Milk Marketing Order.  In
              general, milk produced within a milk marketing area stays within the area
              (USDA 1994).  However, these marketing areas are generally ven. large.  For
              example, the Eastern Ohio-Western Pennsylvania milk marketing area covers
              the eastern third of Ohio, the western third of Pennsylvania, and the Wesi
              Virginia panhandle,  as shown in Figure 1.  USDA milk marketing data for this
              area were reviewed  to estimate the fraction of milk produced in the area
              surrounding the WTI facility that is sent to the large, federally inspected milk
              processing facilities  contained within the Eastern Ohio-Western Pennsylvania
              milk marketing area.
                    Based on milk marketing data for Beaver County, Pennsylvania (USDA
              1988) and milk production data for the same year  (PDA 1994), it is estimated
              that approximately 85 percent of the milk produced in Beaver County in
              December 1988 was processed in the federally inspected plants (i.e..  15
              percent remains local).  No data were available for the other two counties
              (Columbiana and Hancock); therefore, Beaver County data are assumed to
              apply to the entire three-county area.  Table 21 presents the estimated amount
              of milk that is produced and remains in the three-county area surrounding the
              WTI facility.
                    To estimate the amount of locally derived milk that is available for
              consumption in the area surrounding the WTI facility, the milk that remains
              local (including milk consumed on farm, milk sold directly to  consumers, and
              milk processed locally) was  compared to the total annual consumption in the
              three-county area surrounding the facility.  The amount of milk that remains
              local is estimated in  Table 21 as 32.3 million pounds. However, the
              Pennsylvania Department of Agriculture statistics (PDA 1994) indicate that
              approximately 50 percent of the fluid milk produced is used in the production
              of dairy products.  Therefore, from Table 21, a total of 16.2 million pounds of
              locally produced fluid milk is available for consumption annually in the three-
              county area surrounding the WTI facility.
                    Based on age-specific population data within the three-county area
              (Table 14) and age-specific milk consumption rates (Table 18), the  total annual
              milk consumption  in the three-county area is 57.9  million pounds.   Therefore,
              an additional 41.7 million pounds of milk are required from the large.  non-

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              local processing plants to make up the shortfall (i.e.. 57.9 million pounds
              minus 16.2 million pounds).  USDA (1988) data indicate  that the three
              counties surrounding the WTI facility accounted for approximately five percent
              of the total milk processed in the non-local, federally inspected milk
              processing plants in the Eastern Ohio-Western Pennsylvania milk marketing
              area.  Therefore, the total amount of milk that is produced locally and is
              available for local consumption is 18.3 million pounds (i.e.,  16.2 million Ibs
              + [0.05 x 41.7 million Ibs]).
                     The total amount of milk from locally raised cows represents 32
              percent of the total milk consumption for the area surrounding the WTI faciht\
              (i.e., 18.3 million lbs/57.9 million Ibs). Because data on  milk products
              (cheese, butter, etc) production are very limited for the three-county area
              surrounding the WTI facility, the fraction of milk products consumed that is
              derived from locally raised cows was also assumed  to be 0.32. The high-end
              value of the fraction of milk consumed that is derived from locally raised cows
              is assumed to be twice the average value.
                     For farmers, typical and high-end values for the fraction of milk and
              milk products ingested  from a local source of 0.44 and 0.75,  respectively, are
              derived from U.S. EPA (1990a) guidance, and are based on data for farm
              families.  It was also assumed that a  subgroup of farmers  may exist that derive
              all their milk and milk  products from their own farm (subsistence farmers).  A
              value of 1 (i.e., 100 percent) is applied for this exposure subgroup of
              subsistence farmers.

       6.      Consumption of Locally-Grown Vegetables and Fruits
              Exposure to chemicals may occur through the consumption of vegetables
       grown in the vicinity of the facility.  The extent of exposure to chemicals through this
       pathway is dependent on:  1) the chemical concentration in the vegetables; 2) the
       vegetable ingestion rate; 3) the fraction of vegetables ingested that comes from a local
       source; and  4) the frequency and duration of exposure.  Exposure factors for this
       pathway are presented in Tables 22 and 23 and are discussed below.
              Based on data collected by the East Liverpool Board of Health for the area
       surrounding  the facility, approximately 30 percent of the local residents have home
       gardens.  This exposure pathway applies only to that portion of the residential
       subgroup.  Exposure is also assessed for local farmers.
Volume V
Appendix V-8
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              a.     Vegetable and Fruit Consumption Rate
                     Median total fruit and total vegetable consumption rates for children (1
              to 6 years old), school children (7 to 12 years old), and adults, obtained from
              the 1987-88 USDA (1993a) survey are summarized in Table 24.  For children.
              median total fruit and total vegetable consumption rates are estimated based on
              a weighted average of consumption rates for 1 to 2-year-old and 3 to 5-year-
              old children (based on the percentage of the survey population in each group)
              Total fruit and total vegetable consumption rates for school-aged children are
              based on weighted averages for 6 to 11-year-old girls and 6 to 11-year-old
              boys.   Adult consumption rates are based on the weighted average of adult
              (older than 20 years) males and females.
                     Vegetable consumption was assumed to be divided among four
              vegetable types:

                     1)     Root vegetables - including below ground vegetables, such as
                           carrots, potatoes, and onions;
                     2)     Leafy vegetable - including vegetables with leafy,  edible
                           surfaces exposed to the atmosphere, such as  lettuce and
                           broccoli;
                     3)     Above ground protected - including vegetables with the edible
                           surface not exposed to the atmosphere,  such  as com.  and,
                     4)     Above ground exposed -  including non-leafy vegetables with
                           edible surfaces exposed to the atmosphere, such as tomatoes and
                           green peppers.

                     The distribution of consumption  rates for these different categories of
              vegetables and fruits are  estimated based on consumption rates (in units of g
              food/kg body weight/day) for more than 100 fruits and vegetables in the
              Dietary Risk Evaluation System (DRES) compiled by U.S.  EPA.  DRES  was
              developed by the Office of Pesticide  Programs (OPP) based on a 1977-78
              USDA  (1982) food consumption survey. A copy  of these data were obtained
              from OPP and were analyzed to estimate the relative consumption rates of the
              total fruit and total vegetable categories. Based on these data, an individual's
              vegetable diet is estimated to be comprised of 38 percent root vegetables,  13
                                                                 X'1*
              percent leafy vegetables,  16 percent protected vegetables, and 33 percent
              exposed vegetables.  For fruits, only two types are identified: protected and
              exposed.  The distribution of fruit consumption between these two types is
Volume V
Appendix V-8
-------
               estimated to be 58 percent protected and 42 percent exposed, based on an
               evaluation of DRES.
                     High-end fruit and vegetable consumption rates are not available from
               the USDA (1993a) data.  Therefore, to estimate the upper end of the fruit and
               vegetable consumption distributions, a method recommended by FDA (1993) is
               applied in which the estimated median consumption rates are multiplied b\ an
               estimated 90th percentile consumption rate to  median consumption rate ratio.
               Actual total fruit or total vegetable consumption distributions are not available:
               however, FDA (1993) estimates that the 90th  percentile to median ratios for
               foods, in general, are typically in the range of 2.0 to 3.0.  In addition, a
               review Pao et al. (USDA 1982) consumption rate distribution data for several
               individual fruits and vegetables (i.e., not all fruits and vegetables combined),
               indicated that the 90th percentile to median ratio for these individual fruits and
               vegetables generally fell  in this range.  For total fruits and total vegetables.
               therefore, a 90th percentile to median ratio of 2.5 is used.  The estimated
               high-end total fruit and total vegetable consumption rates are shown in Table
               24.

              b.     Exposure Frequency
                     The USDA consumption data are based on daily consumption of
              vegetables; therefore, the exposure frequency is assumed to be 350 days per
              year as recommended by U.S. EPA (1991).

              c.   _   Fraction Ingested from Contaminated Source
                     The fraction of an individual's vegetable diet that  is homegrown is
              estimated based on data collected by the East Liverpool Board of Health in a
              local vegetable garden survey.  These data indicate that typically 25 percent of
              a gardening individual's total vegetable diet is  homegrown (50th percentile of
              respondents).  A high-end estimate based on the 90th percentile of respondents
              indicates  that 50 percent of a gardening individual's total  vegetable diet is
              homegrown.
                    For fruits, more that 90 percent of the respondents indicated that less
              than 25 percent of their fruit diet was homegrown; therefore, a value of 25
              percent is used for the high-end value.  For the typical value, it is  estimated
              that 12.5  percent (i.e., half of the high-end  value) of an individual's fruit diet
              is locally  grown.
Volume V
Appendix V-8                              17
-------
                    No data for farm families are available: therefore, the values cited
             above for families with gardens are used.  It is also assumed that a  subgroup
             of farmers may exist that derive all their vegetables from their own  farm. A
             value of 1 (i.e., 100 percent) is applied for this exposure subgroup of
             subsistence farmers.

      7.     Ingestion of Fish
             As indicated in the HHRA (Chapter VII. Section C.2), it is unlikely that local
      residents are exposed to fish caught locally to a significant degree: however, a
      subgroup within the local population that derives  100 percent of their fish diet from
      locally caught fish (referred to as subsistence fishermen) may exist.  It should  be
      noted; however, that no data or information are available to confirm the existence of
      this subgroup.
             The following factors must be considered when estimating exposure to  this
      subgroup: 1) the chemical concentration in fish; 2)  the rate of fish ingestion 3) the
      fraction of fish consumed that were caught locally;  and 4) the frequency and duration
      of exposure.  Values of the exposure  factors for this pathway are presented in Table
      25.  The fish ingestion rate  for this subgroup is based on consumption values for
      recreational fishermen presented by U.S. EPA (1990a). A fish consumption rate of
      30  g/day is used for the typical value. 140 g/day  as the high-end value.  In addition,
      it is assumed that 100 percent of fish  consumed are from the study area.

      8.     Ingestion of Surface Water During Swimming
             It is possible that local residents and fanners may ingest surface water while
      swimming in local surface water bodies. This water may  be contaminated  and may.
      therefore, be a source of exposure to  chemicals.  The extent of exposure to
      contaminated surface water depends upon:  1) the  concentration of chemical in  the
      surface water; 2) water ingestion  rate: and 3)  the exposure time, frequency, and
      duration.  The values of the exposure factors for this  pathway are presented in  Tables
      26  and 27 and are discussed below.

             a.     Ingestion Rate
                    U.S. EPA (1990a) provides  limited data concerning ingestion of surface
             water during swimming.  A value of 0.05 L/hr (50 mL/hr) is assumed  to
             apply. This value is applied as both the typical and high-end surface water
             ingestion rate for all exposure subgroups.
Volume V
Appendix V-8                              i c
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              b.    Exposure Time and Frequency
                    U.S. EPA (1992b) recommends typical and high-end exposure time
              values of 0.5 hr/day and 1 hr/day, respectively.  In addition, typical and high-
              end exposure frequency values of 5 days/year and 150 days/ year are suggested
              (U.S. EPA 1992b).  The U.S. EPA document notes, however, that these data
              are based on judgment. As indicated in Chapter VTJI, this pathway does not
              appear to present significant risk. No further effort, therefore, to collect site-
              specific data was put forth.

       9.     Dermal Contact with  Surface Water During Swimming
              It is possible that local residents and farmers may swim in local bodies of
       surface water and be exposed  to chemicals  from the water through dermal contact.
       The extent of exposure to contaminated  surface water depends upon: 1) the dose per
       swimming event  (which is based on the  chemical concentration in surface water, the
       permeability coefficient of the chemical, and the duration of the swimming event); 2)
       skin surface area; and  3) the exposure frequency and duration.  The values of the
       exposure factors  for this pathway are presented in Tables 28 and 29 and are discussed
       below .

             a.     Absorbed Dose per Event
                    U.S. EPA (1992b)  recommends  two methods for estimating the
             absorbed dose associated with dermal exposure to substances during
             swimming. For inorganic compounds, a steady-state approach is
             recommended using the following equation:
                                                                               (V-9-1)

             where:
                                 =     absorbed dose per swimming event, mg/cnr-event
                    Kp           =     permeability coefficient from water, cm/hr
                    CW          =     concentration in surface water, mg/cm3
                    ET           =     exposure time of event, hr/event

             The value of Kp is estimated to be 0.001 cm/hr, as recommended by U.S.
             EPA (1992b).  The concentration in surface water is estimated as described in
             Appendix V-7.  U.S. EPA (1992b) recommends typical and high-end exposure
             time values of 0.5 hr/day and  1 hr/day, respectively.

Volume V
Appendix V-8                             10
-------
                    For organic compounds. U.S. EPA (1992b) recommends a non-stead%-
              state method of estimating DA^,. as described in. Dermal Exposure
              Assessment: Principles and Applications (U.S. EPA 1992b). This
              methodology is used in the HHRA. The value of the permeability coefficient.
              Kp, for organic compounds is chemical-specific.  Non-steady state values of K..
              are estimated based on a methodology suggested by U.S. EPA (1992b) and are
              presented in Table 30 for the substances of potential concern.  The use of the
              non-steady-state methodology is recommended by U.S. EPA because of the
              generally brief duration of exposure events.

              b.     Skin Surface Area
                    It is assumed that during swimming, the entire body surface would be
              exposed  to the surface water.  Age-specific body surface areas of 18.150 cnr
              for adults, 7,200 cm2 for children, and 10,400 cm2 for school-age children.
              were compiled  from U.S. EPA (1990a) guidance.

              c.     Exposure Frequency
                    Typical  and high-end exposure frequency values of 5 days/year and 150
              days/year are recommended (U.S.  EPA  1992b).  As indicated in Chapter Vm.
              this pathway does not appear to present significant risk.  No further effort,
              therefore, to collect site-specific data was put forth.

       10.     Ingestion of Breast Milk
              It is possible that breast-feeding infants living in the vicinity of the facility may
       be exposed indirectly to  chemical emissions from the stack through ingestion of
       contaminated breast milk.  The magnitude of exposure for this pathway is based on
       the following: 1) concentration of chemical in breast milk; 2) ingestion rate; 3)  the
       exposure duration; 4) the body weight of the infant; and 5) the fraction of
       contaminant ingested that is absorbed.  Based on Smith (1987), typical and high-end
       ingestion rates of breast  milk of 700 g/day and  850 g/day were estimated.  Typical
       and  high-end exposure durations for breast feeding of 90 days and 365 days,
       respectively, are estimated.  Average and  high-end body weights for an infant are
       estimated to be 6 kilograms and 9 kilograms, respectively.  The fraction of
       contaminant absorbed is  estimated to be 0.9.  Values of the exposure factors for this
                                                                 x'*
       pathway are presented  in Table 31.
Volume V
Appendix V-8
-------
        11.    Ingestion of Meat from Locally Hunted Deer
              It is possible that individuals hunting in the area surrounding the WTT facility
        and consuming meat from deer hunted in these areas may be indirectly exposed to
        substances released from  the WTI facility stack.  The magnitude of exposure for this
        pathway is based on the following: 1) concentration of chemical in deer meat:
        2) ingestion  rate; and 3) the exposure duration.  Values of the exposure factors for
        this pathway are presented in Table 32.
              An ingestion rate of 15 g/day is estimated based on the deer harvest (ODNR
        1994; PDNR 1994; WVDNR 1994a, personal communication) in the three counties
        (Columbiana, Beaver, and Hancock) surrounding the WTI facility, the number of
        hunting licenses issued  (ODNR 1994; PDNR 1994; WVDNR  1995; personal
        communication) in each of these three counties, and an estimate of 40 pounds of meat
       per deer (WVDNR 1994).  Table 33 summarizes these values and the estimated
        amount of available deer meat in the three county area.  Assuming that the amount of
       deer meat available is divided equally amongst all hunters with b'censes, the average
       deer meat consumption rate is 15 g/day.  A high-end value of 100 g/day is estimated
       based on the assumption that an individual hunter might consume the meat from two
       deer over the period of a year.  The exposure duration for a resident, 9 and 30 years
       for the average  and high-end, respectively, is assumed to apply to the hunter.
Volume V
Appendix V-8                             71
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                                 REFERENCES
CACI Marketing, Inc. (CACI).  1992.  The sourcebook of county demographics: Census
      edition, Volume one. Arlington, Virginia.

Distad. W.E.  1992.  The Ohio Packing Plant Task Force Governor's Report.

Hawley, J.K.  1985.  Assessment of health risks from exposure to contaminated soil. Risk
      Analysis 5(4):289-301.

LaGoy, P.K. 1987.  Estimated soil ingestion rates for use in risk assessments.  Risk
      Analysis 7(3):355-359.

Ohio Department of Agriculture (ODA).  1994.  Stale of Ohio Department of Agriculture
      1993 annual report and agricultural statistics.

Ohio Department of Natural Resources (ODNR).  1994b. Telephone conversation with L.
      Culbertson, Division of Wildlife, regarding hunting practices in Ohio.  November.

Pennsylvania Department of Agriculture (PDA).   1994.  1992-1993 statistical summary and
      Pennsylvania Department of Agriculture annual report.  Pennsylvania Agricultural
      Statistics Service. Harrisburg, Pennsylvania.  PASS-112

Pennsylvania Department of Natural Resources (PDNR).  1994. Telephone conversation
      regarding deer hunting practices  in Pennsylvania.

Personal Communication.  August 1994. Telephone interviews with county agriculture
      extension agents representing the following counties: Carroll, Columbiana, and
      Jefferson,  Ohio;  Beaver, Washington, and  Lawrence, Pennsylvania; and Hancock and
      Brooke, West Virginia.

Smith, A.H.  1987.  Infant exposure assessment for breast milk dioxins and furans derived
      from waste incineration emissions.  Risk Analysis  7(3):347-353.

U.S. Department of Agriculture (USDA).  1982.  Foods commonly eaten by individuals:
      Amount eaten per day and per eating occasion.  Pao, E.M., K.H. Fleming, P.M.
      Guenther, and S.J.  Mickel.  Home Economics Research Report No. 44.

U.S. Department of Agriculture (USDA).  1988.  December 1988, county-specific milk
      marketing data provided by  Ed Coughlin, National Milk Producers Federation.
      Original reference not available.
Volume V
Appendix V-8
-------
 U.S. Department of Agriculture (USDA).  1993a.  Food and nurriem intakes by individuals
       in the United States, 1 day, 1987-88.  Human Nutrition Information Service.  NFCS
       Rep. No. 87-1-1. September.

 U.S. Department of Agriculture (USDA).  1993b.  Food consumption, prices, and
       expenditures, 1970-92.  Economic Research Service.  Statistical Bulletin Number 867.
       September.

 U.S. Department of Agriculture (USDA).  1994.  Federal milk order market statistics. 1993
       annual summary. Agricultural Marketing Service.  Statistical Bulletin Number 88b.
       August.

 U.S. Department of Commerce (USDC).  1993a.  1992 Census of Agriculture. Volume 1
       Geographic Area Series, Part 35, Ohio, State and County Data.  AC92-A-35.

 U.S. Department of Commerce (USDC).  1993b.  1992 Census of Agriculture, Volume 1
       Geographic Area Series, Part 38, Pennsylvania, State and County Data.  AC92-A-38.

 U.S. Department of Commerce (USDC).  1993c.  1992 Census of Agriculture, Volume 1
       Geographic Area Series, Part 48, West Virginia, State and County Data.  AC92-A-
       48.

 U.S. Environmental  Protection Agency  (U.S. EPA).  1989.  Risk assessment guidance for
       Superfund, Volume I, Human health evaluation manual (Pan A).  Office of
       Emergency and Remedial Response. Washington, D.C.  U.S. EPA 540/1-89/002.

 U.S. Environmental  Protection Agency  (U.S. EPA).  1990a.  Exposure factors handbook.
       Exposure  Assessment Group, Office of Health and Environmental Assessment,
       Washington, D.C.  U.S. EPA/600/8-89/043.

 U.S. Environmental  Protection Agency  (U.S. EPA).  1990b.  Methodology for assessing
       health risks associated with indirect exposure to combustor emissions.  Environmental
       Criteria and Assessment  Office, Office of Health and Environmental Assessment,
       Office of Research and Development.  Cincinnati, Ohio. January 1990.  U.S.
       EPA/600/6-90/003.

 U.S. Environmental Protection Agency (U.S. EPA).   1991.  Human health evaluation
       manual, supplemental guidance:  standard default exposure factors.  Office of Solid
       Waste and Emergency Response.  March 25,  1991.  OSWER Directive 9285.6-03.
Volume V
Appendix V-8
-------
 U.S. Environmental Protection Agency (U.S. EPA).  1992a.  Guidelines for exposure
       assessment; Notice.  Federal Register Vol. 57, No. 104, 22887-22938. May 29,
       1992.

 U.S. Environmental Protection Agency (U.S. EPA).  1992b.  Dermal exposure assessment:
       Principles and applications. Office of Health and Environmental Assessment.
       Washington, D.C.  January 1992.  U.S. EPA/600/8-91701 IB.

 U.S. Food and Drug Administration. (FDA).  1993.  Toxicological principles for the safety
       assessment of direct food additives and color additives used in food, "Redbook H".
       Center for Food Safety and Applied Nutrition.

 West Virginia Department of Agriculture (WVDA). 1994.  West Virginia agricultural
       statistics.  Agricultural Statistics Service, Bulletin No. 24.

 West Virginia Department of Natural Resources (WVDNR).  1994. 1993 Big game bulletin.

 West Virgnina Department of Natural Resources (WVDNR).  1995.  Letter from W.
       Kordek, Technical Support Unit, regarding deer hunting information in West
       Virginina. January 11.
Volume V
Appendix V-8
-------
TABLE 1
Typical Exposure Assumptions for Inhalation of Air
Parameter
CA = Chemical Concentration in Air (mg/m1)
IR = Inhalation Rate (mVhr)
ET = Exposure Time (hr/day)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner"
Chemical-Specific
0.833h
24
350
9"
70h
25,550
3,285
0.667b
24
350
6
15"
25,550
2,190
0.833s
24
350
6
31"
25,550
2,190
0.833h
24
350
20h
70h
25,550
7,300
Child of
Fanner"

0.667h
24
350
6
15"
25,550
2,190
Moles
a - Exposure to subsistence farmers is the name as the exposure to farmers (children and adults).
b - Source U S EPA I990a
Volume V
Appendix V-8
25
-------
TABLE 2
High-End Exposure Assumptions for Inhalation of Air
Parameter
CA = Chemical Concentration in Air (ing/m1)
IR = Inhalation Rate (mVhr)
ET = Exposure Time (hr/day)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner3
Child of
Farmer"
Chemical -Specific
0.833b
24
350
30"
70"
25,550
10,950
0.667h
24
350
6
15"
25,550
2,190
0.833"
24
350
6
31"
25,550
2,190
0.833s
24
350
40h
70h
25,550
14,600
0.667h
24
350
6
15"
25,550
2,190
Notes
a - Exposure 10 subnistence farmers is Ihe same as (he exposure lo farmers (Linldren and adults)
b - Source U S EPA !990«
Volume V
Appendix V-8
26
-------
Volume V
Appendix V
TABLE 3
Typical Exposure Assumptions for Soil Ingeslion
Parameter
CS = Chemical Concentration in Soil (mg/kg)
1R = Ingestion Rate (mg/day)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age Adult Child of
Child Fanner" Fanner"
Chemical-Specific
25"
350f
9h
70*
25,550
3,285
100C
350'
6
15"
25,550
2,190
30d I00r/25c 100° |
350f 175/175U 350' |
6 20h 6
31h 70h 15h
25,550 25,550 25,550
2,190 7,300 2,190 |
Notes
a Exposure to subsistence farmers is the same as the exposure to farmers (children and adults)
b - Source LaOoy 1987 as c.led in U S F.PA I990b
c . US EPA 1990b provides a range of soil ingestion rates for children of 100 mg/day to 200 mg/day The lower hound of this range is used for
typical value
d - Based on indoor and outdoor soil ingestion values for "older children" cited by U S EPA (I990a). The method used for estimating value in table is
provided in text.
e - Exposure for a farmer is divided between field work and non field work. The typical soil ingestion rate for field work was assumed to he equivalent
to high-end adult residential ingestion rate The typical non field work soil ingestion rate was assumed to he equivalent to the typical adult
residential soil ingestion rale
f - Because soil ingestion was assumed to occur both indoors and outdoors, an exposure frequency of 350 days/year was assumed to apply
g - Exposure frequency was divided equally between outdoor field work and non-field work; therefore, the average soil ingestion rate for a fanner over
^ the period of at least a year is 62 5 g/day, based on the field and non field ingestion rates and exposure frequencies.
h - Source U S EPA 1990a
-8 27


-------
                                                                                TABLE  4
                                                        High-End Exposure  Assumptions for Soil Ingestion
Parameter
CS = Chemical Concentration in Soil (mg/kg)
IR = Ingestion Rate (mg/day)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner"
Child of
Farmer"
Chemical-Specific
100b
350f
30h
70"
25,550
10,950
200°
350'
6
15"
25,550
2,190
6tf
350'
6
3,h
25,550
2,190
480c/100r
175/175r'«
40h
70h
25,550
14,600
200C
350'
6
15"
25,550
2,190
               Notes
               b -
               c -
               d -
                f-
                g -
Exposure to subsistence farmers is the same a.s the exposure to farmers (children and adults).
"Upper hmind" tiled in  U  S  EPA 1991
U S  EPA I990H provides a range of soil mgestion rales for children of 100 mg/day to 200 mg/day.  The upper hound of this range was used for the
high  end value
Based on indoor and outdoor soil inpestion values for "older children" cited by U S. EPA (I990a)  The method used for estimating value in table is
provided in text.
Exposure for a farmer is divided between field work and non-field work   The high-end estimate of soil mgestion for field work is based on U.S.
EPA guidance for outdoor workers (U S  EPA 1991)  The high-end non field work soil ingestinn rate was assumed to be equivalent to the high-end
residential soil ingestion rate
Because soil ingestion was assumed to occur both indoors and outdoors, an exposure frequency of 350 days/year was assumed to apply
Exposure frequency was divided equally between outdoor field work and non-field work; therefore, the high end soil ingestion rate for a farmer over
the period of at least a year is 290 g/day, based  on the field and non-field ingestion  rales and exposure frequencies
Source. U.S. EPA I990a
Volume  V
Appendix V-8
                                                            28
-------
TABLE 5
Typical Exposure Assumptions for Dermal Contact with Soil

Parameter
CS = Chemical Concentration in Soil (mg/kg)
SA = Skin Surface Area Available for Contact (cm2)
AF = Soil to Skin Adherence Factor (mg/cm2-day)
ABS = Absorption Factor (unitless)
EF = Exposure Frequency (day/yr)
ED = Exposure Duration Cyr)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner"
Child of
Fanner"
Chemical -Speci fie
l,890h
0.2C
970h
0.2°
l,330h
0.2"
1 ,890h
0.2c/1.0d
970h
0.2C
0 Or for metals; 0 03C for dioxin like compounds; 0 Of? for organic compounds
350'
9e
70'
25,550
3,285
350*
6
15«
25,550
2,190
350=
6
31'
25,550
2,190
175/175cJ
20*
70"
25,550
7,300
35(T
6
15'
25,550
2,190
Notes-
a - Exposure to subsistence farmers is the same as the exposure to farmers (children and adults).
b - Assumed typical skin surface area based on exposure to hands and forearms (U.S EPA I990a).
c - Source- U.S EPA 1992b
d - The high-end soil to skin adherence factor was assumed to apply to a farmer working in the field.
e - The exposure frequency for dermal contact was assumed to be the same as for soil ingestion.
f - Exposure frequency was equally divided between outdoor field work and non field work; therefore the average value of the adherence factor over the
period of at least a year is 0 6 mg/crrf-day
*g - Source: U.S. EPA 1990a
Volume V
Appendix V-8
29
-------
TABLE 6
High-End Exposure Assumptions for Dennal Contact with Soil
Parameter
CS = Chemical Concentration in Soil (mg/kg)
SA = Skin Surface Area Available for Contact (cm2)
AF = Soil to Skin Adherence Factor (mg/cm'-day)
ABS = Absorption Factor (unitless)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yr)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner*
Child of
Fanner"
Chemical-Specific
4,950h
1.0C
2,440s
1.0"
3,700h
1.0C
4,950h
1.0C
2,440K
I.O1
0 Ol1 for metals; 0 03e for dioxin-like compounds, U (\& for organic compounds
350'1
30<
7(T
25,550
10,950
350-1
6
15'
25,550
2,190
35V
6
31r
25,550
2,190
350d
4cr
7(T
25,550
14,600
350-1
6
LV
25,550
2,190
Notes
a - Exposure to subsistence farmers PS the same as ihe exposure to farmers (children and adulls)
b - Assumed high-end based on exposure to hands, forearms, am hall Ihe head and legs (U.S EPA I990«).
c - Source U S EPA I992b
d - The exposure frequency for dermal contact was assumed to the same as for soil ingeslion
e - Source: U.S EPA I990a
Volume V
Appendix V-8
30
-------
TABLE 7
Typical Exposure Assumptions for Consumption of Locally Raised Meat and Eggs

Parameter

CB = Chemical Concentration in Meat (mg/kg)
IR = Ingestion Rate (g/day)
FI = Fraction of Meat Ingested from
Contaminated Source" (unitless)
Beef
Pork
Chicken
Other Poultry
Eggs
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)

Adult
Resident

Child
Resident

School-Age
Child

Adult
Farmer

Child of
Farmer
Subsistence
Fanner
Adult
Subsistence
Farmer
Child
' Chemical-Specific
See Table 9


0.15
0.18
0
0
0.16
350
9"
70"
25,550
3,285


0.15
0.18
0
0
0.16
350
6
15"
25,550
2,190


0.15
0.18
0
0
0.16
350
6
31"
25,550
2,190


0.44b
0.44
0.44
0.44
0.44
350
20"
70"
25,550
7,300


0.44b
0.44
0.44
0.44
0.44
350
6
15"
25,550
2,190


1
I
1
1
1
350
20h
70h
25,550
7,300







350
6
15"
25,550
2,190
Notes:
a - Method used to estimate fraction of meat ingested from contaminated source, FI, for residential population subgroups is outlined in text.
b - Source: US. EPA I990a.
Volume V
Appendix V-8
31
-------
TABLF 8
High-End Exposure Assumptions for Consumption of Locally Raised Meat and Eggs

Parameter

CB = Chemical Concentration in Meat (mg/kg)
IR = Ingestion Rate (g/day)
Fl = Fraction of Meat Ingested from
Contaminated Source' (unitless)
Beef
fork
Chicken
Other Poultry
L:ggs
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)

Adult
Resident

Child
Resident

School-Age
Child

Adult
Fanner

Child of
Farmer
Subsistence
Farmer
Adult
Subsistence
Fanner
Child
, Chemical -Specific
See Table 9


0 30
0 36
0
0
0.32
350
30h
70h
25,550
10,950


0.30
0.36
0
0
0.32
350
6
15h
25,550
2,190


0.30
0.36
0
0
0.32
350
6
31"
25,550
2,190


0.75"
0.75
0.75
0.75
0.75
350
40"
70h
25,550
14,600


0.75h
0.75
0.75
0.75
0.75
350
6
15"
25,550
2,190


1
1
1
1
1
350
40h
70h
25,550
14,600


1
1
1
1
1
350
6
15"
25,550
2,190
Notes-
» - Method used to estimate the fraction of meat ingested from contaminated source, Fl, for residential population subgroups is outlined in text.
b - Source: U.S. EPA 1990a.
Volume V
Appendix V-8
32
-------
TABLE 9
Meat and Eggs Consumption Rates
Food
Beef
Pork
Chicken
Other Poultry
Eggs
Typical Consumption Rate
(g/day)'
Child0
27
23
31
5
12
School-Age
Child
57
27
48
7
15
Adulf
81
34
48
13
22
High-End Consumption Rate
(g/da>)"
Childc
62
64
68
11
26
School-Age
Child
137
68
106
'15
35
Adult'
20?
95
loti
29
51
Notes-
a - Based on USDA 1993a
b - Based on USDA 1982
c - Applies to children of residents, farmers, and subsistence farmers
d - Applies to residents, farmers, and subsistence farmers
Volume V
Appendix V-8
-------
TABLE 10
90th Percentiie to Median Food Consumption Ratios
Food
Child
School- Age
Child
Adult
Meat and Eggs
Beef
Pork
Chicken
Other Poultry
Eggs
2.3
2.8
2.2
2.2
2.2
2.4
2.5
2 2
2.2
2.3
2.5
2.8
-> -i
.. *•» "i
2.3
1
Milk Products
Milk and Milk Drinks
Cheese
Milk Desserts
Yogurt
Cream
Butter
2.0
2.8
2.2
2.5"
NA
2.8
1.9
2.8
2.3
2.5"
4.3b
2.8
3.0
2.4
2.4
2.3
4.3
3.8
Vegetables'
Vegetables
2.5
2.5
2.5
Fruits'
Fruits
2.5
2.5
2.5
Notes
NA - Not applicable The 90th percentlle to median ratio was not calculated because the food consumption
rate was zero
a - Limited distribution data for child and school-age child consumption of yogurt, a value of 2.5 was
assumed.
b - No distnbutlon data for school-age consumption of cream, adult ratio assumed to apply
c - The 90th percentlle to median ratio for total fruits and toul vegetables was estimated to be 2 5 based
on 90th percentlle/ median ratios for individual fruits and vegeubies estimated by USDA (1982)
Volume V
Appendix V-8
-------
                                                      TABLE 11
                                              State-wide Beef Statistics
                Parameter
                                                                Number of Head  (thousands)
                                                    Ohio'
                                                             Pennsylvania*
                         West Virginia'
   Total Cattle/Calves (C,.)
                                         1,610
     1,850
      520
   Plant Cattle Slaughter (PS^J
                                          185
      969
229b (estimate)
   Calves Bom (B)
                                         560
      780
     250
   Plant Calf Slaughter (PSMlf)
                                          62
      168
     NA
38C (estimate)
   Notes
    NA -
    b -
Nol available
Sute-wide agncultural statistics obtained from the Agricultural Statistics Service for Ohio, Pennsylvania, and West Virginia
(ODA 1994; PDA 1994; WVDA 1994). Total cattle/calves data are for January 1. 1993; all other data «re for most recent
calendar year available.
This value is an estimate of the number of Pennsylvania-bred cattle that are slaughtered in the state. 740 thousand head
slaughtered annually in two large, eastern Pennsylvania slaughter houses are not included in this number
Calf slaughter data were not available for West Virginia; it was assumed that 15 percent of the calves born were
slaughtered, based on the average of Ohio and Pennsylvania data
Volume V
Appendix V-8
-------
TABLE 12
Estimated County Beef Statistics
Parameter
Total Cattle/Calves'
Plant Cattle Slaughter1"
Calves Bornc
Plant Calf Slaughter*
Number of Head in County
Columbiana,
Ohio
26.000
3.000
9.000
1.000
Beaver,
Pennsylvania
11.500
1.400
4,800
1.000
Hancock.
West Virginia
1.200
37
580
87-
Note-
a - County-specific data available: ODA 1994, PDA 1994; WVDA 1994. January 1. 1993
b - Based on state-wide data. PS^/C,. x total cattle in county
c - Based on state-wide data: B/Cr x total cattle in county
d - Based on state-wide dau : PS^B x estimated number of calves in county
Volume V
Appendix V-8
-------
TABLE 13
Annual Availability of Beef from Locally Raised Cattle
State/County
Columbiana
Beaver
Hancock
Estimated
Cattle
Slaughtered3
(head/yr)
3,000
1.400
37
Estimated
Calves
Slaughtered"
(head/yr)
1.000
1.000
87
TOTAL
Estimated
Beef from
Cattle"
(pounds/yr)
1.650.000
840.000
18,500
2,508.500
Estimated
Beef from
Calves'
(pounds/yr)
250.000
200.000
19,575
469.575 . "
Total Local
Beef
Available
(pounds/\ r)
1.900.000
1.040.000
38.075
2.978.075
Notes
a - see Table 12
b - Beef available per head of cattle was assumed to be one-half average cattle live weight. Live weights for cattle were
assumed to be 1,100 Ibs Ohio, 1,200 Ibs Perm., 1,000 Ibs West Virginia (ODA 1994; PDA 1994. WVDA 19941
c - Beef available per calf was assumed to be one-half average calf live weight. Live weights for calves were assumed to be
500 Ohio, and 400 Ibs Pennsylvania (ODA 1994; PDA 1994) Average live weight for West Virginia calves assumed to be
450 Ibs
Volume V
Appendix V-8
T.1
-------
                                            TABLE 14
                                     Age-Specific Population in
                                        Three-County Area
          Countv
                                                        Population'
                                 Children
                                 (1 - 6 yrs)
                      School-Age
                      (7 - 12 yrs)
                        Adults
                        >13 \rs)
   Columbiana, Ohio
 9.225
 9.485
 89.550
   Beaver, Pennsylvania
14.366
14.813
156.914
   Hancock. West Virginia
 2,325
2.692
30.216
                TOTAL
25,932
27.702
276.683
  Note
          CACI 1992
Volume V
Appendix V-8
-------
                                                      TABLE 15
                             Available Pork and Eggs from Locally Raised Livestock
                                                          Pork
County
Columbiana, Ohio
Beaver, Pennsylvania
Hancock, West Virginia
Fraction of
State Hog
Herd'
0.003
0.0017
0.003
Estimated Annual
Hog Slaughter"
(head)
8.457
3.744
59
TOTAL
Estimated Annual
Pork Available'
(pounds)
1.074.000
442.000
11.000
1,527.000
                                                          Eggs
County
Columbiana, Ohio
Beaver, Pennsylvania
Hancock, West Virginia
Estimated
Number of
Layers
16.400"
8.800*
150f
Estimated Annual
Egg Production*
(103 Eggs)
4.412
2,385
32
TOTAL
Annual
Eggs Available*1
(pounds)
552.000
298.000
4.000
854.000
           Notes
            a -       Based on State Agricultural Statistics data (ODA 1994. PDA 1994, WVDA 1994)
            b -       Estimated based on the product of the fraction of state hog herd in each county and the number of hogs
                     slaughtered annually in state (ODA 1994. PDA 1994. WVDA 1994)
            c -       Pork available per hog was assumed to be one-half average hog live weight  Live weights for hogs
                     assumed to be  254 Ibs for Ohio. 236 Ibs for Pennsylvania, 368 Ibs for West Virginia (ODA 1994.
                     PDA 1994. WVDA 1994)
            d -       Number of layers for Columbiana Counry estimated from the ratio of layers (PDA 1994) to chicken
                     farms (USDC 1993b)  in Beaver Counrv and the number of chicken farms in Columbiana Counry
                     (USDC 1993a)
            e -       PDA (1994)
            f -       Based on extrapolation of 1987 dau (# of lavers/*  of chicken farms) for county (USDC 1993c) and
                     1992 census of chicken farms (USDC 1993ci
            g -       Estimated based on the average annual egg  production per layer: 269 for Ohio, 271 for Pennsylvania.
                     215 for West Virginia (ODA 1994. PDA 19<"  WVDA 1994)
            h -       Estimated based on 1.5 pounds/dozen eggs  (TJSDA 1993b)
Volume V
Appendix V-8
-------
TABLE 16
Typical Exposure Assumptions for Consumption of Locally-Produced Milk Products
Parameter
CM = Chemical Concentration in Milk
Product (mg/kg)
IR = Ingestion Rate (g/day)
FI = Fraction of Milk Product Ingested
from Contaminated Source
FF = Exposure Frequency (days/yr)
I-D = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Farmer
Child
Fanner
Subsistence
Farmer
Adult
Subsistence
Fanner
Child
Chemical-Specific
See Table 1 8
0.36'
350
9h
70b
25,550
3,285
0.36'
350
6
15"
25,550
2,190
0.36"
350
6
31s
25,550
2,190
0.40"
350
20s
70s
25,550
7,300
0.40s
350
6
15"
25,550
2,190
1
350
20h
70"
25,550
7,300
1
350
6
I5h
25,550
2,190
Notes
a - Method of estimation outlined in text
b Source U S. EPA 1990s
Volume V
Appendix V-8
40
-------
TABLE 17
High-End Exposure Assumptions for Consumption of Locally-Produced Milk Products
Parameter
CM = Chemical Concentration in Milk
(mg/kg)
IR = Ingestion Rate (g/day)
FJ = Fraction of Milk Ingested from
Contaminated Source
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner
Child
Farmer
Subsistence
Fanner
Adult
Subsistence
Fanner
Child
Site-Specific
See Table 18
0.72"
350
30s
70"
25,550
10,950
0.72'
350
6
15s
25,550
2,190
0.72'
350
6
31"
25,550
2,190
0.75b
350
40h
70h
25,550
14,600
0.75"
350
6
15"
25,550
2,190
1
350
40h
70"
25,550
14,600
1
350
6
15"
25,550
2,190
Notes.
a - Assumed to he two limes the average value
b - Source U S EPA 1990s
Volume V
Appendix V-8
41
-------
TABLE 18
Milk and Milk Product Consumption Rates
Food
Milk and Milk Drinks
Cheese
Milk Desserts
Yogurt
Cream
Butter
Typical Consumption Rate
(g/day)
Child'
391
8
17
7
0
2
School- Age
Child
407
9
35
5
2
4
Adult"
184
16
20
6
4
6
High-End Consumption Rate
(g/day)
Child'
782
•»i
39
18
0
6
School-Age
Child
773
25
81
13
9
11
Adulr
*52
38
48
14
17
23
Notes.
a - Based on USDA (1993a)
b- Based on USDA (1982)
c - Applies to children of residents, farmers, and subsistence farmers
d - Applies to residents, farmers, and subsistence farmers
Volume V
Appendix V-8
-------
TABLE 19
State-wide Milk Data1

Milk Cows (x 103 head)
Milk Production (x 106 Ibs)
Marketing (x 106 Ibs)
Fed to Calves on Farm
Consumed on Farm
Sold to Plants/Dealers
Sold to Consumers
Ohio
315
4.625
4.625
20
15
NA"
(4.470)
NAb
(120)
Pennsylvania
655
10,364
10.364
70
30
9.999
265
West Virginia
23
278
278
4
1
NA"
(265)
NA"
(7)
Notes
a - Slate-wide agricultural statistics obtained from the Agricultural Statistics Service for Ohio, Pennsylvania, and West Virginia
fODA 1994; PDA 1994; WVDA 1994).
b - Available Ohio and West Virginia sales data were not divided between sales to plants/dealers and direct sales to consumers
The numbers in parenthesis represent estimated values based on the distribution of sales between sales to Plants/ dealers and
direct sales to consumers exhibited in Pennsylvania data.
Volume V
Appendix V-8
-------
TABLE 20
Estimated County Dairy Statistics1

Milk Cowsb
Milk Production (x 103 Ibs)
Columbians,
Ohio
11,800
179,800C
Beaver,
Pennsylvania
3.000
41.700"
Hancock.
West Virginia
<50
604'
Marketing' (x 103 Ibs)
Fed to Calves on Farm
Consumed on Farm
Sold to Plants/Dealers
Sold to Consumers
770
580
173,800
4,700
280
120
40.200
1,100
9
4
576
15
Notes:
a - County data estimated based on state data and the fraction of the total state herd in county.
b - ODA 1994; PDA 1994; WVDA 1994
c - Available Ohio agricultural statistics provide county-specific data on milk sold. Milk production was estimated
based on state-wide data.
d - PDA 1994
e - Estimated based on fraction of state milk cow herd in county multiplied by the total milk produced in the slate
f - Marketing values do not necessarily sum to total production due to rounding
Volume V
Annendiv V-R
-------
TABLE 21
Availability of Milk from Locally Raised Cows
State/Count}
Columbiana
Beaver
Hancock
Milk
Consumed
on Farm"
(x 103 Ibs)
580
120
4
Milk Sold
Directly to
Consumer*
(x 10s Ibs)
4,700
1,100
15
Milk
Processed
Locallvb
(x 1(P Ibs)
20.970
4.755
63
Total Milk
Total for Fluid Milk-"
Total Local
Milk
Available1
(x 10* Ibs)
26.250
5.975
82
32,307
16.154
Notes
a - see Table 20
b - Milk (pounds) sold to Plants/Dealers (Table 20) minus [0.85 x milk production ^pounds)].
c - Sum of milk that is consumed on farm, milk that is sold directly to consumers, and milk processed localK
d - 50 percent of milk produced is assumed to go to dairy product production
Volume V
Appendix V-8
-------
TABLE 22
Typical Exposure Assumptions for Consumption of Locally Crown Fruits and Vegetables

Parameter

CV = Chemical Concentration in
Vegetables (mg/kg)
IR = Ingestion Rate (g/day)
Fl = Fraction of Vegetable Diet that
is Homegrown"
Vegetables
Fruit
EF = Exposure Frequency (days/yr)
F.D = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
(with Garden)
Child
Resident
(with Garden)
School-Age
Child
(with Garden)

Adult
Farmer

Child
Farmer
Subsistence
Fanner
Adult
Subsistence
Fanner
Child

Chemical-Specific
See Table 24


0 25
0 125
350
9h
70h
25,550
3,285


0.25
0.125
350
6
15s
25,550
2,190


0.25
0.125
350
6
31"
25,550
2,190


0.25
0.125
350
20h
70b
25,550
7,300


0.25
0.125
350
6
15"
25,550
2,190


1
1
350
20h
70b
25,550
7,300


1
1
350
6
15s
25,550
2,190
Notes
a - Based on the median of responses from the vegetable/fruit garden survey conducted by the East Liverpool Board of Health.
b - Source U S EPA I990a
Volume V
Appendix V-8
46
-------
TABLE 23
High-End Exposure Assumptions for Consumption of Locally Grown Fruits and Vegetables
Parameter
CV = Chemical Concentration in
Vegetables (mg/kg)
IR = Ingestion Rate (g/day)
FI = Fraction of Vegetable Diet that
is Homegrown"
Vegetables
Fruit
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
'AT = Averaging Time (days)
Adult
Resident
(with Garden)
Child
Resident
(with Garden)
School-Age
Child
(with Garden)
Adult
Fanner
Child
Fanner
Subsistence
Fanner
Adult
Subsistence
Fanner
Child
Chemical-Specific
See Table 24
0.5
0.25
350
30"
70s
25,550
10,950
0.5
0.25
350
6
15"
25,550
2,190
0.5
0.25
350
6
31"
25,550
2,190
0.5
0.25
350
40"
70b
25,550
14,600
0.5
0.25
350
6
15"
25,550
2,190
1
1
350
40h
70"
25,550
14,600
1
1
350
6
15"
25,550
2,190
Notes-
a - Based on the high end (90th percentile) of responses to the vegetable/fruit garden survey conducted by the East Liverpool Board of Health
b - Source: U S EPA I990a
Volume V
Appendix V-8
47
-------
TABLE 24
Fruit and Vegetable Consumption Rates
Food
Typical Consumption Rate'
Childc
School- Age
Child
Adulf
High-End Consumption Rate~
Child'
School-Age
Child
Adult*
Vegetables (g/day)
Total Vegetables
Aboveground Exposed
Aboveground Protected
Leafy
Root
83
27
13
11
32
129
43
21
17
49
206
68
33
27
78
208
68
33
21
79
323
106
." 52
42
123
515
170
82
6T
196
Fruits (g/day)
Total Fruits
Exposed
Protected
155
65
90
168
71
97
137
58
79
388
163
225
420
176
244
343
144
199
Notes
a - Based on USDA (1993»)
h- Based on USDA (19821
c - Applies to children of residents, farmers, and subsistence farmers
d - Applies to residents, fanners, and subsistence tanners
Volume V
Appendix V-8
-------
TABLE 25
Typical and High-end Exposure Assumptions for Ingestion of Fish
by Subsistence Fisherman
Parameter
CF =
IR =
FC =
EF =
ED =
BW =
LT =
AT =
Notes
a -
b -
Chemical Concentration in Fish (mg/kg)
Ingestion Rate (g/day)
Fraction of Fish Caught Locally (unitless)
Exposure Frequency (days/yr)
Exposure Duration (yrs)
Body Weight (kg)
Lifetime (days)
Averaging Time (days)
Average
Values
High-end
Values
Chemical -spec i fi c
30"
1.0
350
9"
70"
25.550
3,285
140"
1.0
350
30°
70b
25.550
10.950
Based on recreational fisherman consumption value presented by U.S. EPA (1990a)
Source: U.S EPA 1990s
Volume V
Appendix V-8
-------
TABLE 26
Typical Exposure Assumptions for digestion of Surface Water During Swimming
Parameter
CW = Surface Water Concentration (mg/L)
IR = Ingestion Rate (L/hr)
ET = Exposure Time (hr/day)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner"
Child of
Fanner"
Chemical-Specific
0.05h
0.5C
5C
9"
70*1
25,550
3,285
0.05b
0.5'
5C
6
15*
25,550
2,190
0.05h
0.5°
5C
6
3ld
25,550
2,190
0.05h
0.51
5C
20d
70d
25,550
7,300
0.05h
0.51
5C
6
15"
25,550
2,190
Mole*
a - Exposure 1" subsistence farmers is the surne ns the exposure to farmers (children and adults)
h - Source U S FPA I9R9
c - Source U S EPA IWh
d - Source- U S EPA !990a
Volume V
Appendix V-8
50
-------
TABLE 27
High-End Exposure Assumptions for Ingestion of Surface Water During Swimming
Parameter
CW = Surface Water Concentration (mg/L)
IR = Ingestion Rale (L/hr)
ET = Exposure Time (hr/day)
EF = Exposure Frequency (days/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner*
Child of
Fanner"
Chemical-Specific
0.05h
lc
I50C
30"
1&
25,550
10,950
0.05h
lc
I50C
6
15d
25,550
2,190
0.05h
lc
150C
6
31"
25,550
2,190
0.05h
lc
150C
40d
70d
25,550
14,600
0.05b
lc
150C
6
15"
25,550
2,190
Moles
• Exposure lo subsidence farmers is ihe same as the exposure to farmers (children and adults)
h - Source U S EPA 1989
c - Source' V S EPA I992h, high end eslimale of exposure
d - Source U S EPA I990a
Volume V
Appendix V-8
51
-------
TABLE 28
Typical Exposure Assumptions for Dermal Contact with Surface Water During Swimming
Parameter
D \mai Absorbed dose per swimming event (mg/cm'-event)
CW = Surface Water Concentration (mg/cm1)
Ky = Permeability Coefficient (cm/hr)
ET = Exposure Time (hr/event)
SA = Skin Surface Area Available for Contact (cnv)
EF = Exposure Frequency (events/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Fanner3
Child of
Fanner1
Chemical-Specific
Chemical-Specific
Chemical-Specific (see Table 30)
0.5'
18,150"
5C
9>
70"
25,550
3,285
0.5°
7,200b
5°
6
IS-1
25,550
2,190
0.5'
10.40011
5°
6 -
31"
25,550
2,190
0.5°
18,l50h
5C
20d
70"
25,550
7,300
0.5"
7,200h
y
6
I5d
25,550
2,190
Notes
a - Exposure to subsistence farmers is the same as the exposure to farmers (children and adults)
h - Source- U S EPA 1990s (entire body surface area)
c - Source V S EPA I992a
d - Source: U.S EPA 1990s
Volume V
Appendix V-8
52
-------
TABLE 29
High-End Exposure Assumptions for Dermal Contact with Surface Water During Swimming
Parameter
DAevl.nl Absorbed dose per swimming event (mg/cm:-event)
CW = Surface Water Concentration (mg/cm1)
K,, = Permeability Coefficient (cm/hr)
ET = Exposure Time (hr/event)
SA = Skin Surface Area Available for Contact (cm3)
EF = Exposure Frequency (events/yr)
ED = Exposure Duration (yrs)
BW = Body Weight (kg)
LT = Lifetime (days)
AT = Averaging Time (days)
Adult
Resident
Child
Resident
School-Age
Child
Adult
Farmer"
Child of
Fanner"
Chemical -Spec! fie
Chemical -Spec! fie
Chemical -Specific (see Table 30)
1°
18,150b
150C
30"
70"1
25,550
10,950
1"
7,200h
150°
6
15d
25,550
2,190
1°
10,400b
I50C
6
3,d
25,550
2,190
lc
I8.15011
150°
40d
70d
25,550
14,600
r
7,200H
I50C
6
15d
25,550
2,190
Notes:
« - Exposure lo subsistence farmers is the same as the exposure to farmers (children «nd adults).
b - Source. U S EPA 1990a (entire body surface area)
c - Source U S EPA 1992a
d - Source: U.S. EPA I990a
Volume V
Appendix V-8
53
-------
Volum
Appen
TABLE 30
Chemical-specific Kp Values
Substance
Permeability coefficient
from water (Kp)J
(cm/hr)
Dioxins and Furans
2.3.7.8-TCDD
1,2.3.7.8-PeCDD
1, 2.3,4,7, 8-HxCDD
1,2.3.6.7,8-HxCDD
1,2,3.7,8.9-HxCDD
1.2. 3.4.6.7. 8-HpCDD
OCDD
2,3.7.8-TCDF
1, 2,3,7, 8-PeCDF
2,3,4,7,8-PeCDF
1,2,3.4.7. 8-HxCDF

1,2.3.6.7,8-HxCDF
1,2.3.7.8,9-HxCDF

2,3.4.6.7.8-HxCDF
1.2.3.4.6,7.8-HpCDF

1,2.3.4. 7. 8.9-HpCDF
OCDF
1.07
0.66
2.67
1.20
2.67
3.22
0.72
1.12
1.06
1.31
1.50
1.50
1.50
1.50
2.47
2.47
6.53
PICs and Residues of Organic Compounds
Tetrachlorobiphenyl
Hexachlorobiphenyl
Heptachlorobiphenyl
Benzol a Ipyrene
Benzorb)fluoranthene
Bis(2-ethylhexyl)phthalate
Carbon tetrachloride
Dibenz(a.h)anthracene
Di(n)octyl phthalate
Heptachlor
Hexachlorobenzcne
Hexachlorobutadiene
Hexachloropentadiene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
0.81
1.48
2.13
1.20
1.39
1.20
0.02
2.15
4.17
0.28
0.53
0.13
0.28
1.42
2.06
e V
dix V-8 54
-------
TABLE 30
Chemical-specific Kp Values
Substance
Penmeabilit> coefficient
from water (Kp)'
(cm/hr)
Metals
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (trivalent)
Chromium (hexavalent)
Copper
Lead
Mercury
Nickel
Selenium
Silver
Thallium
Zinc
1 x 10-'
1 x 10-'
1 x 10-'
1 x 10'3
1 x 10';
1 x 10-'
1 x 10-'
1 x 10'
1 x 10-'
1 x 10-'
1 x ID'3
1 x 10-'
1 x JO'3
1 x 10 '
1 x ID'3
1 x 10'3
Noie
a - Kp estimated based on methodology descnbed by U S EPA (1992b)
Volume V
Appendix V-
55
-------
TABLE 31
Typical and High-End Exposure Assumptions for Ingestion of Breast Milk
Parameter
CM =
f , =
IR =
ED =
BW =
LT =
AT =
Notes
a -
b -
Chemical Concentration in Breast Milk (rag/kg)
Fraction of ingested contaminant that is absorbed (unitless)
Ingestion Rate (g/day)
Exposure Duration (days)
Body Weight (kg)
Lifetime (days)
Averaging Time (days)
Breast Feeding Infant
Typical
High-End
Chemical-Specific
0.9
700*
90°
6"
25.550
90
0 o
850"
365"
9h
25.550
365
Smith (1987) provides ranges of infant breast milk intake of 677 to 922 mL/day and 723 to 751 g/day from two studies
Typical and high-end values of 700 g/day and 850 g/day, respectively, are estimated based on these data.
Assumption.
Volume V
Appendix V-8
56
-------
TABLE 32
Typical and High-End Exposure Assumptions for Ingestion of Deer Meat Consumption b\ Hunter
Parameter
CM =
IR =
EF =
ED =
BW =
LT =
AT =
Notes
a -
h -
Chemical Concentration in Deer Meat (mg/kg)
Ingestion Rate (g/day)
Exposure Frequency (days/yr)
Exposure Duration (yr)
Body Weight (kg)
Lifetime (days)
Averaging Time (days)
Typical
High-End
Chemical-Specific
15'
350
9"
70b
25.550 '
3.285
100-
350
30-
70"
25.550
10.950
Estimation method outlined in text
Source U.S EPA 1990s
Volume V
Appendix V-
                                            57
-------
TABLE 33
Estimation of Meat from Deer Hunted Locally
County
Columbiana
Beaver
Hancock
TOTAL
Annual Deer Harvest"
2,149
4.452
787
7,388
Deer Meat Available''
(Ibs)
85.960
178.080
31.480
295.520
Number of Hunters0
4.315
17.013
3.365
24.693
Notes.
a - ODNR 1994, PDNR 1994, WVDNR 1995
b- Deer harvest x 40 Ibs per deer (AWDNR 1994a)
e - Based on the number of hunting licenses (ODNR 1994, PDNR 1994. WVDNR 1995)
Volume V
Appendix V-8
58
-------
TABLE 34
Key Assumptions in Estimation of Exposure Factors
Assumption
Exposure pathways have been adequately identified and
characterized >
Exposure factors represent the behavior of the various
populations
The soil ingestion rate for school-age children is
divided between indoor and outdoor rates and prorated
because indoor exposure occurs year round and outdoor
exposure only occurs during the warmer months (200
days/year with temperatures exceeding 50° F)
The soil ingestion rate for farmers is prorated to include
a higher ingestion rate during periods of outdoor field
work and a lower rate during non-field activities
The exposure frequency for soil ingestion occurs 350
days/year implying that incidental soil ingestion occurs
both indoors and outdoors
For dermal contact with soil, exposure occurs to the
hands and forearms in the average case and includes
half the head and legs in the high-end case
The absorption factor for dermal contact with soil uses
the upper end of the ranges recommended by U.S. EPA
(1992) for dioxin-like, organic and inorganic
compounds, based on one chemical in each class
Consumption of lamb/veal/game and organ meats is not
considered in meat ingestion rates
Basis
Exposure pathways are consistent with U.S. EPA guidance
(e.g., U.S. EPA 1989) and site-specific evaluation.
Site-specific values are used whenever possible, otherwise,
U.S. EPA-default values are used - the 50th percentile for
average exposures and the 90th percentile for high-end
exposures.
Conservative assumption based on professional judgment.
Conservative assumption based on professional judgment.
Conservative assumption based on professional judgment.
Conservative assumption based on professional judgment.
Conservative assumption based on best available data.
Consumption rates for these categories of meats are
insignificant.
Magnitude
of Effect
low
medium
low
low
low
low
low
low
Direction of
Effect
underestimate
overestimate
overestimate
overestimate
overestimate
overestimate
overestimate
underestimate
Volume V
Appendix V-8
59
-------
TABLE 34
Key Assumptions in Estimation of Exposure Factors
Assumption
The high end of the food consumption distribution is
estimated as the product of median consumption rates
and the ratio of the 90th percentile to the median of
individual food consumption rates presented in USDA
(1982)
Slate wide beef and dairy cow statistics are applied at
the local level
Beef cattle slaughtered within a county is consumed
within the same county
The amount of beef derived from each head of
slaughtered cattle is 50 percent of the average live
weight of cattle slaughtered in the state
An analysis of the data similar lo the one for beef is
applied to other meat products to determine the fraction
that is raised locally
Locally raised chickens and uirkey make up an
insignificant portion of a typical resident's diet
Farm families derive a significant portion (0.44 and
0.75 for average and high-end exposures, respectively)
of their meat and milk products from locally raised
livestock
Subsistence farmers derive all of their meat and milk
products from locally raised livestock
Basis
Conservative assumption based on professional judgment.
Professional judgment on best available data.
Professional judgment.
Professional judgment on best available data.
Professional judgment.
Based on local agricultural census data (USDC 1993a,b,c)
that indicate that very few chicken farms are located in the
area
U.S. EPA (I990a) guidance
Conservative assumption based on professional judgment. -
Magnitude
of Effect
low
low
low
low
low
low
low
medium
Direction of
Effect
overestimate
overestimate
overestimate
unknown
unknown
underestimate
unknown
overestimate
Volume V
Appendix V-8
60
-------
TABLE 34
Key Assumptions in Estimation of Exposure Factors
Assumption
The butter consumption rate includes margarine and
butter substitutes, items that do not contain dairy '
products
The Beaver County milk production data apply to the
whole study area
The Fast Liverpool Board of Health estimates that 30
percent of the local resident have home gardens. Their
survey of 100 residents with gardens is representative
of local gardening practices and provides reasonable
data to estimate the fraction of diet that is homegrown.
The fraction ingested from contaminated sources
estimated for families with gardens apply to farm
families
Concentrations of contaminants are equal in outdoor soil
and indoor house dust.
Ingestion of deer meat rates is estimated based on
dividing the amount of deer meat available from an
annual harvest by the number of hunters with licenses
(average exposure) and one hunter consuming two deer
in a year (high-end exposure)
Basis
Conservative assumption based on professional judgment.
Professional judgment on best available data.
Professional judgment on best available data.
Professional judgment, no available data.
Professional judgment, no available data.
Professional judgment on best available data.
Magnitude
of Effect
low
low
low
low
low
low
Direction of
Effect
overestimate
t
unknown
unknown
unknown
unknown
variable
Moles
low = less than a factor of two II
medium = a factor of two to ten 1
high = greater than a factor of ten
Volume V
Appendix V-8
61
-------
tr
LLJ
o
o
X
3
<
c
o
cr
                                                         PENNSYLVANIA
                                         WEST
                                        VIRGINIA
O
                    EASTERN OHIO/ WESTERN PENNSYLVANIA
                       FEDERAL MILK MARKETING AREA
                                                                      Figure
                                                                        1
-------
                           APPENDIX V-9

                    Review of USDA Milk Marketing Data
Volume V
Appendix V-Q
-------
 SUMMARY OF MILK MARKETING DATA

       This appendix summarizes milk marketing data obtained from a number of sources
 and identifies its use in developing estimates of milk distribution in the risk assessment stud>
 area.  These milk marketing/distribution data are used to develop an estimate of the fraction
 of milk consumed by local residents that is derived from locally raised cows.  The  area of
 interest for which data were collected was limited to the three counties (Columbiana. Ohio:
 Beaver, Pennsylvania; and Hancock, West Virginia) in the immediate vicinity of the WTI
 facility to coincide with the risk assessment  study area.
       Milk  marketing data compiled from the Departments of Agriculture in Ohio,
 Pennsylvania, and West Virginia are summarized in Table  1.  These data include information
 on local consumption (e.g., on farm) and milk marketing to plants/dealers and directly to
 consumers.   Discussions with the agricultural extension agents in Columbiana County. Ohio;
 Beaver County, Pennsylvania; and Hancock County, West  Virginia (personal
 communication), indicated that milk that is marketed to plants and dealers (shown in Table 1)
 is divided between large processing facilities that are not generally located in the area and
 smaller, local processing facilities that  generally service communities within 5 to 10 miles of
 the processing facility.
       To estimate the distribution of milk between the large processing facilities and the
 local handlers,  a USDA (1988) milk marketing report that  summarizes county-by-county and
 state contributions to federally inspected milk processing plants (these are the large
 processing facilities referred to above)  was reviewed.   Federally inspected milk processing
 plants are assigned to different "milk marketing areas" under the Federal Milk Marketing
 Order.  Irr general, milk produced within a milk marketing area stays within the area (USDA
 1994).  However,  these marketing areas are  generally very large.  For example, the Eastern
 Ohio-Western Pennsylvania milk marketing area covers the eastern third of Ohio, the western
 third of Pennsylvania, and the West Virginia panhandle.  USDA milk marketing data for this
 area are reviewed to estimate the fraction of milk produced in the area surrounding the WTI
 facility that is sent to the large, federally inspected milk processing facilities contained within
the Eastern Ohio-Western  Pennsylvania milk marketing area.
       Based on milk marketing data for Beaver County, Pennsylvania (USDA 1988) and
milk production data for the same year (PDA 1994), it was estimated that approximately 85
percent of the milk produced in Beaver  County in December 1988 was processed in the
federally inspected plants (i.e., 15 percent remains local).   No data were available  for the

Volume V
Appendix  V-9                              i
-------
TABLE 1
Estimated County Dairy Statistics2
Parameter
Milk Cowsb
Milk Production (x 103 Ibs)
Columbiana,
Ohio
11,800
179.800C
Beaver,
Pennsylvania
3.000
41.700"
Hancock.
West Virginia
<50
604'
Marketingf (x 103 Ibs)
Fed to Calves on Farm
Consumed on Farm
Sold to Plants/Dealers
Sold to Consumers
770
580
173,800
4,700
280
120
40.200
1,100
9
4
576
15
[
Notes:
a - County data estimated based on state data and the fraction of the total state herd in counn .
b - ODA 1994; PDA 1994; WVDA 1994
c - Available Ohao agricultural statistics provide county-specific data on milk sold. Milk production
was estimated based on state-wide data.
d - PDA 1994
e - Estimated based on fraction of state milk cow herd in county multiplied by the total milk produced
in the state.
f - Marketing values do not necessarily sum to total production due to rounding.
Volume V
Appendix V-9
-------
TABLE 2
Availability of Milk from Locally Raised Cows
State/County
Columbiana
Beaver
Hancock
Milk
Consumed
on Farm"
(x 103 Ibs)
580
120
4
Milk Sold
Directly to
Consumer*
(x 103 Ibs)
4,700
1,100
15
Milk
Processed
LocalJyb
(x 103 Ibs)
20.970
4,755
63
Total Milk
Total for Fluid Milkd
Total
Local Milk
Available0
(x l(f Ibs)
26.250
5.975
82
32.307
16.154
Notes:
a - see Table 1
b - Milk (pounds) sold to Plants/Dealers (Table 1) minus 0.85 x milk production (pounds).
c - Sum of milk that is consumed on farm, milk that is sold directly to consumers, and milk
processed locally.
d - 50 percent of milk produced is assumed to go to dairy product production.
Volume V
Appendix V-9
-------
 other two counties (Columbiana and Hancock): therefore. Beaver County data was assumed
 to apply to the entire three-county area.  Table 2 presents the estimated amount of milk that
 is produced and remains in the three-county area surrounding the WTT facility.
       To estimate the amount of locally derived milk that is available for consumption in
 the area surrounding the WTI facility, the milk that remains local (including milk consumed
 on farm, milk sold directly to consumers, and milk processed locally) is compared to the
 total annual consumption in the three-county area surrounding the facility. The amount of
 milk that remains local is estimated in Table 2 as 32.3 million pounds.  However, the
 Pennsylvania Department of Agriculture statistics (PDA 1994) indicate that approximate lv 50
 percent of the fluid milk produced is used in the production of dairy products.  Therefore.
 from  Table 2, a total of  16.2 million pounds of locally  produced fluid milk is available for
 consumption annually in the three-county area surrounding the WTI facility. Based on age-
 specific population data within the three-county area (Table 3) and  age-specific milk
 consumption rates (Table 4), the  total annual milk consumption in the three-county area is
 57.9 million pounds. Therefore, an additional 41.7 million pounds of milk are  required from
 the large, non-local processing plants to  make up the shortfall (i.e., 59.7  million pounds
 minus 16.2 million pounds). USDA  (1988) data indicate that the three counties surrounding
 the WTI facility accounted for approximately five percent of the total milk processed in the
 non-local, federally inspected  milk processing plants in  the Eastern Ohio-Western
 Pennsylvania milk marketing area.  Therefore, the  total amount of milk that is produced
 locally and is available for local consumption is  18.3 million pounds (i.e., 16.2  million Ibs +
 [0.05 x 41.7  million Ibs]).   The total  amount of milk from locally raised cows represents 32
percent of the total milk  consumption for the area surrounding the WTI facility  (i.e.. 18.3
million lbs/59.7 million Ibs).  Because data on milk products (cheese, butter, etc) production
are very limited for the three-county area surrounding the WTI facility, the fraction of milk
products consumed that is derived from locally raised cows is also  assumed to be 0.32.
Volume V
Appendix V-9
-------
                                            TABLE 3
                                     Age-Specific Population in
                                        Three-Countv Area
          County
                                 Children
                                 (1 - 6 yrs)
                                                       Population'
                      School-Age
                      (7 - 12 yrs)
                        Adults
                      (>13 yrs)
   Colurnbiana, Ohio
 9.225
 9.485
 89.566
   Beaver, Pennsylvania
14.366
14.813
156.914
   Hancock. West Virginia
 2.325
2.692
 30.216
                TOTAL
25,932
27,702
276.683
   Note
   a - CACI 1992a
Volume V
Appendix V-9
-------
TABLE 4
Milk and Milk Product Consumption Rates
Food
Milk and Milk Drinks
Cheese
Milk Desserts
Yogurt
Cream
Butter
Typical Consumption Rate"
(g/day)
Child
391
8
17
7
0
2
School- Age
Child
407
9
35
5
2
4
Adult
184
16
20
6
4
6
High-End Consumption Rateh
(g/day)
Child
782
^^
39
18
0
6
School-Age
Child
773
25
81
13
9
11
Adult
55:
3S
48
14
17
23
Notes
a - USDA (1993)
h - USDA (1982)
Volume V
Appendix V-9
-------
                                 REFERENCES
 CACI International, Inc. (CACI).  1992.  The sourcebook of zip code demographics   CACI
       Marketing Systems.  Arlington. VA.

 Ohio Department of Agriculture (ODA).  1994.  Slate of Ohio Depanmeni of Agriculture
       1993 annual report and agricultural statistics.

 Pennsylvania Department of Agriculture (PDA).  1994.  1992-1993 statistical summary and
       Pennsylvania Depanmeni of Agriculture annual report.   Pennsylvania Agricultural
       Statistics Service.  Hanisburg, Pennsylvania.  PASS-112

 Personal Communication. August 1994.  Telephone interviews with county agriculture
       extension agents representing the following counties: Carroll, Columbiana. and
       Jefferson, Ohio; Beaver, Washington, and Lawrence, Pennsylvania; and Hancock and
       Brooke, West Virginia.

 U.S. Department of Agriculture (USDA).   1982. Foods commonly eaten by individuals:
       Amount eaten per day and per eating occasion.  Pao. E.M., K.H. Fleming. P.M.
       Guenther, and S.J. Mickel.  Home Economics Research  Report No. 44.

 United States Department of Agriculture. (USDA).  1988.  December 1988. county-specific
       milk marketing data provided by Ed Coughlin, National Milk Producers  Federation.
       Original reference  not available.

 United States Department of Agriculture. (USDA).  1993.  Food and nutrient intakes by
       individuals in the United States, 1 day, 1987-88.  Human Nutrition Information
       Service.  MFCS Rep.  No. 87-1-1.   September.

 United States Department of  Agriculture. (USDA).  1994.  Federal milk order market
       statistics, 1993 annual summary. Agricultural Marketing Service.  Statistical Bulletin
       Number 886. August.
Volume V
Appendix V-0
-------
                           APPENDIX V-10

                 Milk Production bv ZIP Code and Farm Size
Volume V
Appendix V-10
-------

ZIP Code
—
—
43945
43968
44224
44406
44408
44413
44423
44427
44431
44432
44445
44451
44455
44460
44493
44601
44609
44619
44625


n
2



2
1
1

4
2


8




1
1 - 30,000
dhs)
Production11
-
*•
R



R
R
R

83,674
R


l.:5,661




R
State and County (hy ZIP Code) Milk Production by Farm Size"
30,001 - 60,000
Obs)
n
1
2

1
1
1
2
1
1
6
2

1
8


2
I
6
Production11
*~~
•
R
R

R
R
R
R
R
R
276,619
R

R
375,993


R
R
286,201
60,001 - 90,000
dhs)
n
-". i
2

1

2

6

4
2
2


9


2

4
Production1'
Columhi
:
R

R

R

426,042

305,972
R
R


657,352


R

283,836
90,001 - 120,000
dhs)
n
ana C
1



1

2
1
3
1



6


1

2
Production11
ounty, OH
-
R



R

R
R
309,189
R



604,664


R

R
120,001 - 150,000
dhs)
n
•-
==
2





2
2
1

1

1
1




Production11
-
R





R
R
R

R

R
R




150,001 & over
(Ihs)
n




1

I

2
1
2


5

2
2

1
Production1'




R

R

R
R
R


894,511

R
R

R
Totals hy ZIP
Code
n
4
6
1
1
C
3
12
C
12
15
8
1
1
37
1
2
7
1
14
Production'1
—
300,222
414,535
R
R
520,509
78,452
975,667
410,468
1,342,645
998,270
677,165
R
R
2,718,181'
R
R
80V>77
R
1,01';, 904
Voltime V
Appendix V
10
-------
State and County (hy ZIP Code) Milk Production by Farm Si/e"
ZIP Code
44634
44657
44665
Columbians
County,
Oil
1 - 30,000
(Ibs)
n
1


22
Production11
R


492,698
30,001 - 60,000
(Ihs*
n
7
5

48
Production11
321,951
231,093

2,188,406
60,001 - 90,000
(Ibs)
n
1
2
1
38
Production1'
R
R
R
2,793,815
90,001 - 120,000
(Ibs)
n
1
1

20
Production6
R
R

2,008,339
120,001 - 150,000
(Ibs)
n
3
1

14
Production11
423,750
R

1,929,043
150,001 & over
(Ibs)
n
2
3

22
Production1'
R
850,631

4,769,800
Totals by ZIP
Code
n
15
12
1
164
Production'1
1,358,969
1,458,252
R
14,182,101
Beaver County, PA
15001
1 5005
15009
15010
1 5026
15042
15043
15050
15066
15074
16037
16115
16117

1

2
1

1

1


1
I

R

R
R

R

R


R
R


1
2

2
3
1
4

1
1
1


R
R

R
126,259
R
179,774

R
R
R
1


2

2

2

2



R


R

R

R

R






I
2



1
2






R
R



R
R







1


1









R


R








1












R









1
1
1
8
4
4
4
4
6
4
1
7
7
R
R
R
533,496
351,686
212,322
126,259'
308,188
300,518
142,135
R
R
R
Volume V
Append;- \\Q
-------
State and County (by ZIP Code) Milk Production by Farm Size"
ZIP Code
16120
16123
16141
16232
Beaver
Country,
PA

n

2


10
- 30,000
(Ib.s)
Production11

R


215,490
30,001 - 60,000
dbs>
n
1
2
2

21
Production11
R
R
R

914,075
60,001 - 90,000
(Ibs)
n
1
3

1
14
Production11
R
227,956

R
977,058
90,00! - 120,000
(Ibs)
n

3


9
Production1'

312,622


931,132
120,001 - 150,000
(Ibs)
n

2


4
Production'1

R


518,946
150,001 & over
(Ibs)
n




1
Production1'




R
Totals by ZIP
Code
n
2
12
2
1
59
Production1'
R
947,438
R
R
3,556,701*
Hancock County, WV
No dairy farms listed
Notes
a - US Dcpartr
regarding da
h - Production is
c - Tola! encludt
n - Number of f
R - Restricted, p
nent nf Agriuillure (USDA) t114 Letter from J Rourke, Market Information Branch, Dairy Division, tn D Canter, Office of Solid Waste »nd Emergency Response, U S PPA,
a on number of dairy farmers and milk production in Ohio, Pennsylvania, and West Virginia December 1
pounds of Grade A milk that was marketed
imu
:rtains to the operations of fewer than three farms
Volume V
Appendix V-H)
-------
                               REFERENCES

 U.S. Department of Agriculture (USDA).  1994.  Letter from J. Rourke. Market Information
      Branch, Dairy Division, to D. Canter, Office of Solid Waste and Emergency  Response.
      U.S. EPA.  December 1.
Volume V
Appendix V-10
-------
                            APPENDIX V-ll

                Estimation of Environmental Media Concentrations
Volume V
Appendix V-ll
-------
 TABLE 1   Average Modclrr) FnvitoMmrnt.il Fnposurr Cnnrrnlralmns
Chemical
2,3.7.8-TCDD
1,2,3.7,8-PeCDD
1,2,3.4.7.8 HxCDD
1,2,3,6,7,8 HxCDD
1,2,3,7,8.9 HxCDD
1,2,3,4,6.7,8-HpCDD
OCDD
2,3.7.8-TCDF
1,2,3,7,8-PeCDF
2,3,4, 7,8-PeCDF
1,2.3.4,7.8-HxCDF
1,2,3.6,7,8-HxCDF
1,2,3.7,8,9-HxCDF
2, 3,4,6.7, 8-HxCDF
1,2,3,4.6,7,8 HpCDF
1,2,3.4,7,8,9 HpCDF
OCDF
Tetrachlofobiphenyt
Hexachloroblphenyl
Heptachlorobiphenyl
Beruo(a)pyrene
Benzo(b)riuoranthene
Bls(2-ethythexyl)phthalate
Carbon tetrachloride
Dibenz(a,h)anthracene
Dl(n)octy) phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
?inc
Subarea
S1 avg
SI avg
SI avg
S1 avg
S1 avg
S1 avg
SI avg
SI avg
SI avg
SI avg
S1 avg
S1 avg
S1 avg
S1 avg
S1 avg
S1 avg
51 avg
SI avg
SI avg
SI avg
S1 avg
S1 avg
SI avg
S1 avg
S1 avg
S1 avg
S1 avg
SI avg
S1 avg
S1 avg
S1 avg
S1 avg
S1 avg
SI avg
S1 avg
S1 avg
SI avg
SI avg
SI avg
S1 avg
S1 avg
S1 avg
SI avg
S1 avg
S1 avg
S1 avg
Leafy
Produce
Cone
mg/kgWW
50E-12
90E-11
1 2E-10
3 4E-11
39E-11
2 OE-09
2 6E-07
74E-11
45E-10
60E-10
4 1E-10
94E-10
2 1E-10
68E-10
22E-09
1 7E-10
5 6E-08
66E-10
1 2E 09
3 8E-08
4 2E-06
20E 06
2 3E 03
36E-07
69E-09
44E-04
2 OE-09
1 1E-08
1 1E-08
1 9E-10
3 9E-08
69E-09
1 6E-08
7 1E-08
5 4E-07
36E-11
3 6E-08
7 1E-10
9 9E 08
5 OE-05
5 OE-05
1 2E-08
72E-07
1 1E-07
2 6E-08
2 7E-06
Root
Produce
Cone
mg/kgWW
69E-15
32E-14
1 7E-14
4 2E-14
2 6E-14
1 8E-13
1 2E-12
68E-14
18E-13
20E-13
37E-13
35E-13
83E-14
40E-13
16E-12
2 IE 13
1 9E 12
1 7E-10
2 7E-11
1 6E-10
4 IE 11
1 7E-09
37E-11
1 3E 07
56E-10
3 2E 08
1 6E-11
1 5E-07
46E-08
22E-09
1 3E-07
6 1E-10
63E-12
62E-12
10E-10
37E-16
30E-11
1 9E-14
24E-11
43E-09
43E-09
52E-13
14E 10
75E-11
46E 14
62E-10
River
Fish
Cone
mg/kg
5 1E 12
24E-11
4f\C I 1
UC - 1 1
5DF 1 1
UC 1 1
1 7F 1 1
J £C ' 1 1
7 3E-1 1
56E-12
38E-11
1 9E-10
28E-10
45E-10
42E-10
98E-11
4 7E 10
52E-10
6 7E-11
2 3E-11
3 4E-09
3 OEO7
1 2E 07
55E-07
2 4E-06
3 7E-07
55E-09
30E 05
6 3E-08
96E-09
5 7E-05
39E-06
45E-09
4 9E-07
3 BE 05
39E-11
3 8E 08
7 OE-09
20E-11
8 2E 08
35E-10
2 2E-07
7 OE-05
4 OE 04
63E 09
96E 07
70E-11
1 3E 07
4 4E-07
Lake
Fish
Cone
mg/kg
NA
NA
WA
NA
NA
, k|A
' l^r^
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
30E 16
1 4E 15
3 OC 1 C
oc - 1 o
1 *^F 1 *^
I Dt -ID
O KP 1 C
y Dt - I O
2 1 E- 15
34E 14
29E-15
78E-15
86E-15
1 3E-14
1 2E-14
29E 15
1 4E 14
3 1E 14
39E 15
85E-15
62E-13
5 1E-13
59E-13
9 7E-12
38E-11
1 8E-11
1 8E-10
22E-11
1 OE-12
1 9E-14
1 OE-10
1 2E-10
1 7E-12
98E-11
25E-11
39E-11
85E-10
1 8E-09
1 OE-12
37E 11
22E-11
1 3E-09
1 9E 08
1 9E-08
1 OE 10
1 2E-08
1 4E-10
1 IE 09
1 OE 09
Lake
Water
Cone
mg/L
NA
NA
11 A
NA
k j A
NA
hi A
NA
kj A
P4M
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
' 3E-11
2 1E-10

1 4E-10
3 7E-1 1
5 2E-11
4 2E-10
7 7E-08
4 OE-11
1 9E-10
1 1E-09
59E-10
1 1E-09
2 5E-10
7 2E-10
56E-10
1 1E-10
64E-09
25E-09
1 6E-09
50E-08

1 9E-06
26E-04
1 1E-10
38E-07
29E-04
2 OE-09
93E-09
1 4E-09
88E-11
15E-05
35E-07
1 7E-09
28E-08
9 OE-09
1 3E-11
93E-10
1 6E-09
5 7E 09
93E 08
93E-08
1 1E-08
5 3E-07
2 1E-08
59E-07
1 2E-08
Volume V. Appendix V-11
-------
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                                                                                                                                                                "o
-------
 TABLE 1   Average Morlrlnd Fnvironmrnlnl Fiposuip Conrrnlr.-ilions
Chemical
2,3.7,8-TCDD
1,2.3,7,8 PeCDD
1.2.3.4.7,8-HxCDD
1, 2,3.6,7, 8-HxCDD
1,2,3,7,8,9-HxCDD
1. 2,3,4.6, 7,8-HpCDD
OCOD
2,3,7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4. 7.8-PeCDF
1,2,3,4,7,8-HxCDF
1.2.3,6,7,8-HxCDF

1.2,3,7,8,9-HitCDF
2.3,4,6,7,8 HxCDF
1,2,3.4,6. 7,8 HpCDF
1,2,3,4, 7,8,9-HpCDF
OCDF
Telrachloroblphenyl
Hexaehloroblphenyt
Heptachloroblphenyl
Benzo(a)pyrene
Benzo(b)fluoranthene
Bi«(2-«lhy1hexy1)phthalate
Carbon tetrachloride
Dibenz(a,h)anlhracene
Di(n)oc(yt phlhalale
Heptachlot
Hexachloroberuene
Hexachlorobutadiene
Hexachlorocyclopenladiene
Hexachtorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalerrt)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg

S2 avg
S2 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
S2 avg
52 avg
S2 avg
52 avg
S2 avg
S2 avg
52 avg
52 avg
52 avg
S2 avg
52 avg
S2avg
52 avg
52 avg
52 avg
52 avg
S2 avg
52 avg
S2 avg
52 avg
52 avg
Leafy
Pioduce
Cone
mg/kgWW
23E-12
42E-11
59E-11
1 6E-11
1 8E-11
96E-10
1 2E-07
35E-11
2 1E-10
29E-10
1 9E-10
4 4E-10

1 OE-10
32E-10
1 OE-09
80E-11
26E-08
31E-10
56E-10
1 8E-08
20E-06
96E-07
1 1E^)3
1 7E-07
18E-09
21E-04
92E-10
52E-09
5 OE-09
88E-11
1 1E-08
1 BE -09
4 1E-09
1 8E-08
1 3E-07
92E-12
9 OE-09
1 8E-10
2 5E-08
24E-05
24E 05
30E 09
1 BE 07
2 6E 08
6 7E-09
6 7E-07
Root
Produce
Cone
mg/kg'/WV
29E-15
1 2E 14
52E-15
1 2E-14
7 1F-1"i
t 1 C- 1 ^
47E-14
30E-13
30E-14
72E-14
75E-14
1 1E-13
1 OE-13

26E-14
1 2E-13
46E-13
57E-14
49E-13
8 1E-11
1 3E-11
76E-11
1 6E-11
78E-10
1 3E-11
6 3E-08
1 4E-10
1 5E-08
76E-12
7 2E-08
2 2E-08
1 OE-09
3 4E-08
1 6E-10
16E-12
1 5E-12
25E-11
92E-17
75E-12
46E-15
59E-12
2 OE-09
2 OE-09
1 3E-13
35E-11
1 9E-11
1 1E-14
1 5E-10
River
Fish
Cone
mg/kg
NA
NA
NA
NA
KIA
MrA
NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
KIA
Nr\
, NA
NA
NA
NA
NA
NA
MA
nw
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA
KIA
rlM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA
kl A
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
5 9f£.i2
1 OE-10
6 8E-11
1 7E-11

2 4E-11
2 OE-10
3 6E-08
1 9E-11
88E-11
5 OE-10
2 7E-10

5 1E-10
1 2E-10
3 3E-10
25E-10
49E-11
3 OE-09
1 2E-09
76E-10
23E^)8
1 5E-06
88E-07
1 2E-04
53E-11
1 OE-07
14E-04
96E-10
44E-09
65E-10
41E-11
41E-06
9 3E-08
44E-10
72E-09
23E-09
34E-12
24E-10
4 1E-10
1 5E-09
4 4E-08
4 4E-08
3 OE-09
1 4E 07
55E 09
1 5E 07
3 OE-09
Volume V Anoendu V-11
-------
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                          "5
-------
 7 ABl E  1   Average Mouelrd Fnvirnnmnnlal f 'poMirr Conrrnliahons
Chemical
2.3,7.8 TCDD
1.2.3.7.8 PeCDD
1,2.3,4,7.8-HxCDD
1.2,3.6.7,8 HxCDD
1,2,3,7,8,9-HxCDD
1,2.3.4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4.7,8-PeCDF
1,2,3,4,7,8-HxCDF
1,2,3,6,7.8-HxCDF
1,2,3, 7,8,9-HxCDF
2,3,4,6,7,8-HxCDF
1,2,3,4,6,7,8 HpCDF
1,2.3,4,7,8,9-HpCDF
OCDF
Tetrachlorobiphenyl
Hexachlorobiphenyt
Heplachloroblphenyt
BerHo(a)pyrene
Benzo(b)fluoranthene
Bls(2-ethylhexyl)phthalate
Carbon tetrachlorlde
Dlberu(a,h)anthracene
Dl(n)octy) phthalate
Heptachtof
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopenladiene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
El avg
E1 avg
E1avg
E1avg
El avg
E1 avg
El avg
E1 avg
E1 avg
El avg
El avg
El avg
E1 avg
E1 avg
E1 avg
E1 avg
E1 avg
E1 avg
E1 avg
El avg
E1 avg
El avg
E1 avg
E1 avg
E1 avg
E1 avg
El avg
E1avg
E1 avg
E1avg
E1 avg
E1 avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
E1 avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
E1 avg
El avg
E1 avg
lea'y
Produce
Cone
mg/kgWW
1 OE-11
1 9E-10
26E-10
70E-11
BOE-11
42E-09
5 4E-07
1 5E-10
93E-10
1 3E-09
85E-10
1 9E-09
44E-10
1 4E-09
46E-09
35E-10
1 2E-07
1 4E-09
25E-09
79E-08
88E-06
42E06
4 8E-03
74E-07
1 9E-08
9 1E-04
40E-09
23E-08
2 2E-08
39E-10
1 1E-07
1 9E-08
4 3E-08
1 9E-07
1 4E-06
94E-11
94E 08
19E-09
2 6E-07
1 OE 04
1 OE-04
31E-08
1 9E-06
2 BE 07
6 BE -08
7 1E-06
Root
Produce
Cone
mg/kgWW
1 5E 14
76E-14
46E-14
1 1E-13
72E-14
48E-13
32E-12
15E-13
4 1E-13
47E-13
99E-13
92E-13
2 1E-13
10E-12
44E 12
56E-13
52E-12
36E-10
57E-11
34E-IO
97E-11
34E-09
92E-11
2 8E-07
1 5E-09
6 6E-08
33E-11
3 2E-07
96E-08
46E-09
36E-07
1 7E-09
1 7E-11
1 6E-11
27E-10
97E-16
80E-11
49E-14
62E-11
90E-09
90E-09
1 4E-12
3 7E-10
20E-10
1 2E-13
1 6E 09
River
Fish
Cone
mg/kg
40E-12
19E-11
32E-11
40E-11
26E-11
59E-11
45E-12
3 OE-11
1 5E-10
22E-10
36E-10
33E-10
77E-11
38E-10
42E 10
54E-11
1 9E-11
26E 09
23E-07
9 1E-08
4 4E-07
19E-06
3 OE-07
4 3E-09
2 4E 05
4 9E-08
75E-09
44E-05
30E-06
35E-09
4 OE-07
3 1E-05
3 1E-11
3 OE-08
56E-09
16E-11
6 6E-08
28E-10
1 7E-07
5 4E 05
3 1E-04
50E-09
76E 07
55E-11
1 OE 07
35E 07
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Rivrr
Walet
Cone
mg'L
2 3E 16
1 1E -15
30E 16
1 2E 15
7 7E-16
1 7E-15
2 7E-14
23E-15
6 1E-15
68E-15
1 1E-14
99E-15
23E-15
1 1E-14
24E-14
3 1E-15
68E-15
48E-13
39E-13
46E-13
77E-12
29E-11
1 5E-11
1 4E-10
1 8E-11
78E-13
1 5E-14
81E-11
95E-11
1 3E-12
79E-11
20E-11
3 1E-11
68E-10
1 4E-09
79E-13
30E-11
1 8E-11
1 1E-09
1 5E-08
1 5E-08
8 1E-11
98E 09
1 1E-10
8 7E 10
8 1E 10
lake
Water
Cone
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
26E-11
4 5E-10
30E-10
80E-11
1 1E-10
88E-10
1 6E-07
83E-11
39E-10
22E-09
1 3E-09
23E-09
52E-10
1 5E-09
1 2E-09
24E-10
13E-08
52E-09
33E-09
1 OE-07
66E-06
39E-06
55E-04
23E-10
1 OE-06
6 OE-04
42E-09
1 9E-08
29E-09
1 8E-10
42E-05
96E-07
45E-09
7 3E-08
2 4E-08
34E-11
24E-09
42E-09
1 5E-08
1 9E-07
1 9E-07
3 OE-08
1 4E 06
56E 08
1 6E-06
3 1E-08
Volume V, Appendix V-11
-------
                                                                                                                       I X
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rnmrnrnmmmmrnmmrnmrnmrnrTirnrnmrnrnrnrnrni
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mrnmmmmmrnmrnmmmrammmmmrnrnmmmmmmmmfTimrnmmiTimmrnrTiiTimrnm
                                                                                    immmmmm
O O O
03 -^ -J
 "nrnmmmmmrnrnrnrnnni
                                                                              iru_jk^_.jk-.oo — a>-'iku~-i^jru-.u3
                                                                                                                                           o

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                                                                                                                                        3  n q
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           " n CD

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           ^00

           5 S  5-
                                                                                                                                           n9
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              2 -------
TABLE 1   Average Modeled F rwironmenlal F»posure Concentrations
Chemical
2,3,7.8-TCDD
1.2.3.7.8 PeCDD
1.2.3.4. 7. 8-HxCDD
1,2,3,6,7.8-HxCDD
1,2,3,7. 8,9-HxCDD
1, 2,3.4,6, 7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3, 7,8- PeCDF
2,3,4, 7.8- PeCDF
1.2.3.4,7,8-HxCDF
1.2,3,6,7,8-Hi
-------
  TABLE 1  Average Modrlrd Frwironmrnlal F.posu.p Conrpntral.nns
Chemical


2.3.7.8-TCDD
1.2.3,7,8 PeCDD
1. 2,3.4. 7,8-HxCDD
1,2,3.6.7.8-HxCDD
1.2.3,7.8.9 HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4, 7,8-PeCDF
1,2,3,4,7,8-HxCDF
1.2,3,8,7,8-HxCDF
1,2,3,7,8,9 HxCDF
2,3,4,6,7,8-HxCDF
1.2,3.4,6,7,8 HpCDF
1,2,3,4,7,8,9-HpCDF
OCDF
Tefrachloroblphenyl
Mexachloroblphenyl
Heplachlorobiphenyl
Ben2o(a)pyrene
Benzo(b)nuoran»hene
Bi«(2-ethylhexy1)phthalate
Carbon lelrachloride
Diberu(a,h)anthracene
Di(n)ocry) phthalate
Heptachtor
Hexachlorobenzene
Hexachlorobutadlene
Hexacntorocyclopentadiene
Hexachlorophene
lndeno(1,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
7mc
Subatea


E3 avg
E3 avg
E3avg
E3 avg
E 3 3VQ
E3avg
E3 avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3 avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3 avg
E3 avg
E3 avg
E3 avg
E3avg
E3avg
E3avg
1 cm Soil
Cone
mg/kg

4 9E 11
2 1E-10
2 OE-10
35E 10
2*jc m
£. t- IU
25E-09
1 2E-08
46E-10
1 3E-09
16E-09
32E-09
3 OE-09
7 1E-10
3 4E-09
20E 08
25E 09
3 7E 08
5 7E 08
9 3E 08
9 1E-08
1 IE 06
55E-06
3 7E-07
32E06
20E-06
1 4E-07
27E-09
52E-06
1 4E 05
2 3E-07
54E-06
23E06
4 OE-07
1 6E-05
19E-05
4 1E 08
2 3E 07
1 1E-06
69E 05
2 7E 04
2 7E-04
1 6E-06
29E 04
1 4E-06-
73E-05
1 OE-05
Beel
Cone
mg/kgWW

2 6E 11
45E 10
30E 10
7 7E 11
1 1E-10
88E 10
1 6E-07
83E-11
39E-10
22E09
1 2E-09
23E-09
52E-10
15E 09
1 2E 09
23E 10
1 3E 08
5 7E 09
3 7E 09
1 OE 07
BSE -06
51E 06
7 IE 04
36E-10
83E 07
7 BE 04
55E-09
40E08
72E-09
45E-10
33E-05
76E-07
37E-09
64E-08
20E 08
35E-11
2 OE-09
44E 09
1 5E-08
24E 07
24E 07
27E 08
1 3E 06
4 7E-08
1 7E-06
28E 08
Pofk
Cone
mg/kgWW

6 6E 12
B4E 11
54E 11
1 8E 11
2 3E-11
16E-10
2 7E 08
18E 11
75E 11
42E-10
27E-10
44E 10
10E 10
30E-10
2 7E 10
6 1E-11
23E09
45E-09
2 BE 09
20E 08
56E 07
40E07
46E 05
1 4E-10
9 1E 08
5 IE 05
4 OE-10
36E 08
82E-09
5 OE-10
19E06
94E-08
1 5E-09
2 IE 08
86E-08
29E-11
89E-11
5 7E 09
4 3E 08
8 OE-07
80E 07
1 1E 07
3 IE 05
1 OE 09
70E-06
7 2E 09
Chicken
Cone
mg/kgWW

2 -1C 1 1
Jt 1 J
98E 13
45E-13
6 7E 13
54E-13
99E-13
' 6 BE 12
48E-13
1 1E-12
54E-12
8 1E-12
65E-12
1 6E-12
66E-12
89E-12
2 7E-12
BOE-12
38E-10
23E-10
23E 10
22E-11
1 4E-10
1 1E 12
62E-13
15E 10
24E-12
76E 14
66E-11
1 6E-11
9 1E-13
29E-09
15E-10
1 1E-11
81E-09
32E-11
1 1E-12
36E-10
64E 11
3E 06
5E 07
5E-07
BE 10
OE 06
2E-11
4E 06
63E-09
Fgg
Cone
mg'kgvVW


3 2E 13
1 4E 12
6 3E 13
92E 13
75E 13
1 4E \1
94E 12
66E-13
15E-12
74E-12
1 1E-11
90E 12
22E-12
9 IE 12
1 2E-11
38E-12
1 1E-11
53E-10
3 1E-10
32E 10
2 7E 08
1 7E 07
1 4E-09
78E-10
1 9E 07
30E09
95E-11
8 3E 08
20E-08
1 1E 09
36E 06
1 9E 07
1 3E-10
1 1E 08
26E-08
1 3E-12
86E-12
1 OE-10
1 3E 06
1 3E 08
1 3E 08
28E-10
1 OE 06
24E-10
1 4E 06
63E 09
Milk
Cone
mg kgWW


2 OE 1?
3 4E-11
2 3E-11
58E-12
82E 12
66E-11
1 2E-08
63E-12
29E-11
1 7E-10
92E-11
1 7E-10
39E-11
1 1E-10
88E-11
1 7E-11
1 OE 09
44E-10
28E-10
7 8E-09
34E-06
20E-06
2 8E-04
1 6E-10
3 3E-07
3 1E 04
22E09
1 6E-08
29E-09
1 8E-10
1 3E-05
3 OE-07
4 7E-10
2 4E-09
5 7E 08
39E-14
1 6E-10
15E 09
1 6E 08
39E 07
39E 07
56E 09
24E 06
40E 07
1 1E 07
9 1E 09
Cheese
Cone
mg'kgWW


30E 11
5 IE 10
3 4E 10
B7E 11
1 2E-10
99E 10
1 BE 07
94E 11
44E 10
25E09
14E-09
26E-09
59E-10
1 7E-09
1 3E-09
26E-10
15E-08
65E-09
42E-09
1 2E-07
34E-06
20E-06
28E-04
1 6E-10
3 3E-07
22E-O9
16E-08
29E-09
1 8E-10
1 3E-05
3 OE-07
4 7E-10
24E-09
5 7E-08
39E-14
16E 10
15E09
1 6E-08
39E-07
39E 07
56E 09
24E 06
40E 07
1 IE 07
9 IE 09
Milk
Dessert
Cone
mg/kg WW


1 3E 11
22E-10
1 5E 10
38E-11
53E-11
4 3E-10
7 BE -08
4 IE 11
1 9E-10
1 1E 09
6 OE-10
1 1E-O9
25E-10
73E-10
5 7E-10
1 1E-10
65E-09
28E-09
1 8E-09
5 1E-08
34E-06
20E-06
28E-04
1 6E-10
3 3E-07
3 1E-04
22E-09
16E-08
29E-09
1 8E-10
13E-05
3 OE-07
47E-10
24E-09
5 7E-08
39E-14
16E-10
1 5E-09
1 6E 08
39E 07
39E 07
56E 09
24E 06
40E 07
1 IE 07
9 1E-09
Yoguit
Cone
mg'kgWW


20E 12
34E 11
2 3E-11
58E-12
82E-12
66E-11
1 2E^)8
63E-12
29E-11
1 7E-10
92E 11
1 7E-10
39E-11
1 1E-10
88E-11
1 7E-11
1 OE-09
44E-10
2 BE 10
1 6E-10
33E-07
22EXJ9
1 6EO8
29E-09
1 8E-10
47E-10
24E4)9
57E-08
39E-14
1 6E-10
1 6E-08
39E 07
39E 07
56E 09
24E 06
40E 07
1 IE 07
9 1E 09
Cream
Cone
mg/kgWW


25E 11
4 2E 10
28E-10
7 3E-11
1 OE 10
83E 10
1 5E 07
79E-11
3 7E-10
21E09
1 1E-09
2 1E-09
49E-10
1 4E-09
1 1E 09
22E-10
1 3E-08
54E09
35E-09
9 BE 08
34E-06
20E06
2 BE -04
16E-10
3 3E 07
3 1E-04
22E 09
1 6E-08
29E-09
1 8E-10
1 3E 05
30E07
47E 10
24E 09
5 7E 08
39E 14
16E 10
15E09
1 6E 08
39E 07
39E 07
56E 09
24E 06
40E 07
1 1E 07
9 1F 09
Butler
Cone
md/ko^V^V


82E-11
1 4E-09
93E-10
7 4F 10
£• **t 1 U
34E-10
27E-09
4 9E-07
26E-10
12E-09
69E-09
3 BE 09
7 OE-09
16E-09
46E09
36E-09
71E-10
4 1E 08
1 8E-08
12E-08
3 2E-07
34E-06
20E-06
2 BE -04
1 6E-10
33E-07
3 1E-04
22E-09
16E-08
29E-09
1 8E 10
1 3E-05
3 OE-07
4 7E-10
24E-09
5 7E 08
39E-14
16E-10
15E-09
1 6E-08
39F 07
39E 07
56E 09
2 4E 06
4 OF 07
1 1E 07
9 1 F 09
E»posed
Produce
Cone
mn/bntAAA/
mg/Ky VV W

42E-14
72E 13
99E-13
•\ *\C 4 -I
•J tC- 1 J
33E-13
16E-11
2 OE-09
60E 13
36E-12
48E-12
36E-12
76E-12
1 7E 12
57E-12
20E-11
1 7E-12
44E-10
1 1E-11
1 1E-11
29E-10
3 4E 08
1 BE -08
18E-05
2 BE -07
1 BE -09
34E-06
15E-11
1 7E-09
7 IE 09
47E 11
1 OE 08
1 8E 09
21E 09
1 2E 08
58E08
76E 12
74E 09
2 1E-10
1 7E 08
6 BE 06
68F 06
65E 09
34E 07
1 9E 08
7 f)E 09
1 1F 06
Prolcrled
Produce
Cone
mg/kgWW

32E 15
1 4E-14
29E 15
9 AC 4 C
4E-15
3 IE 15
20E-14
22E 13
35E-14
72E-U-
71E 14
86E-14
80E-14
1 9E-14
91E 14
24E 13
30E-14
1 3E-13
10E 11
30E 12
15E-12
1 4E 10
63E 10
95E 12
49E 07
1 2E 10
1 3E 12
28E 13
28E09
1 2E 08
8 IE 11
1 1E 10
1 4E 10
23E 09
76E09
50E 08
20E 12
76E 09
1 3E 10
1 6E 08
1 2E 05
1 2E 05
9 7E 09
4 3E 07
28E 08
5 7E 10
1 BF 06
Volume V, Appendi

-------
                  )   •/
TABLE 1  Avcragr Mfnlnlrd Fnvirnnmrnlnl F»posurr Cnncrnlt.ilinns
Chemical
2.3,7,8-TCDD
1,2,3,7,8-PeCDD
1,2,3.4.7,8 HxCDD
1,2,3.6,7,8 HxCDD
1,2.3,7,8,9-HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2.3.7,8-PeCDF
2,3,4. 7,8-PeCDF
1,2,3,4,7.8-HxCDF
1.2,3,6,7,8-HxCDF
1.2,3,7,8,9-HxCDF
2.3.4,6,7,8-HxCDF
1,2,3.4,6,7,8-HpCDF
1,2,3,4,7,8,9 HpCDF
OCDF
Tetrachtoroblphenyl
Hexachlofoblphenyl
Heplachloroblphenyl
Benzo(a)pyrene
Beruo(b)f1uoranthene
Bis(2-e1hy1nexyl)ph«nalate
Carbon tetrachlortde
Dlbenz(a ,h)anthracene
Dl(n)octy) phthalate
Heptachtor
Hexachlorobenzene
Hexachlorobutadlene
HexachkHocyclopenladiene
Hexachlorophene
lndeno(1,2,3-cd)pyrene
Anlimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
E3 avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3 avg
E3 avg
E3 avg
E3 avg
E3avg
E3 avg
E3 avg
E3 avg
Leafy
Produce
Cone
mg/kgWW
2 1E 12
39E-11
54E-11
1 5E-11
1 7E-11
88E-10
1 1E-07
32E-11
1 9E-10
26E-10
1 8E-10
40E-10
91E-11
29E-10
95E-10
7 3E-11
2 4E-08
28E-10
5 1E-10
1 6E-08
1 BE-O6
8 7E-07
9 9E-04
1 5E-07
25E-09
19E-04
84E-10
4 7E-09
46E-09
80E-11
1 5E-08
26E-09
61E-09
2 7E-08
2 OE-07
1 4E-11
1 3E-08
27E-10
3 7E-08
22E05
2 2E-05
4 5E-09
2 7E-07
3 9E 08
99E-09
1 OE-06
Root
Produce
Cone
mg/kgWW
29E 15
1 2E-14
65E-15
1 5E-14
96E-15
64E-14
42E-13
29E-14
73E-14
79E-14
1 4E-13
1 3E-13
3 1E-14
1 5E-13
60E-13
76E-14
68E-13
74E-11
1 2E-11
70E-11
1 6E-11
7 1E-10
1 5E-11
57E-08
20E-10
1 4E-08
69E-12
6 6E-08
2 OE-08
94E-10
4 7E-08
22E-10
23E-12
23E-12
37E-11
1 4E-16
1 1E-11
69E-15
88E-12
1 9E-09
1 9E-09
1 9E-13
52E-11
28E-11
1 7E-14
2 3E-10
River
Fish
Cone
mg/kg
46E-13
21E-12
32E-12
39E 12
24E-12
56E-12
42E-13
35E-12
1 6E-11
24E-11
35E-11
33E-11
78E-12
3 7E-11
40E-11
5 1E-12
1 7E-12
32E-10
2 9E 08
1 1E 08
5 2E-08
2 3E-07
4 OE-08
53E-10
25E 06
60E-09
9 1E-10
54E-06
3 7E-07
43E 10
4 4E-08
32E-06
32E-12
30E-09
57E-10
16E-12
79E-09
28E-11
1 7E-08
6 7E 06
38E-05
50E 10
7 6E 08
57E 12
1 OE 08
36E-08
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
, NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
2 7E 17
1 2E-16
3 OE-17
1 1E-16
7 3E-17
1 6E-16
25E-15
27E-16
69E-16
73E-16
1 OE-15
97E-16
23E-16
1 1E-15
24E-15
30E-16
64E-16
59E-14
48E-14
5 7E-14
92E-13
36E-12
20E-12
1 7E-11
19E 12
96E-14
1 8E-15
99E-12
1 2E-11
1 6E-13
88E-12
20E-12
32E 12
68E-11
1 4E-10
78E 14
36E-12
1 7E-12
1 1E-10
1 8E 09
1 8E 09
8 1E 12
9 7E 10
1 1E-11
8 7E-11
84E 11
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
54E 12
92E-11
6 2E-11
1 6E-1,1
22E-T1
1 8E-10
3 3E-08
1 7E-11
80E-11
46E-10
25E-10
4 7E-10
1 1E-10
3 1E-10
24E-10
47E-11
27E-09
1 1E-09
69E-10
21E-08
14E-08
8 OE-07
1 1E-04
48E-11
1 4E-07
1 2E-04
88E-10
40E-09
59E-10
38E-11
57E-06
1 3E-07
65E-10
1 1E-08
34E-09
50E-12
35E-10
6 1E-10
22E-09
40E 08
4 OE-08
4 4E 09
20E 07
8 IE 09
2 2E-07
45E 09
Volume V, Appendix V-11
-------
 "  =  =1
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or a.    P
•O  C
 «!  D
ro
C
LLJ Q.
Butter
Cone
mg/kg
ream
Cone
C
    2*5
    °5f
   > u 01
•*  § v
I  S 5 o.
2  t o *
   C    01
g
Chees
Cone
mg/kgW
Mi
Cn
/kg
                     — iMeoeonv — O) — »«-•» —
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                                                                                          — N.in««D^«-v«-'-coiN'-ioininO)0)'-a>'-r)r)
                                 UJUJUJUJUJUJUJUJUJUJLUUJllJUJUJliJlUUJIAIlUUJUJlUUJllJUJUJUJUJlULUUJ
                                 r>rMCNOOV'-'»»-rM'^o>v'ffUJUJUJU^UJi^
                  cor^'^rsirsir)rij^fr)^-rir^in(Nri»-fno>inir)tDr^r)^-tfiif>^"*- wrN^-cDfniN^-^w-p^^rnrJtDnvincN
                 U'U^'UJUJUJUJUJUJUJUJUJUJUJUJUJUJUJllJUJUJU^U'i^LUU^
                                                                                                                                               - •--
                                 P9»T^"O99Ooo-7Ooooooo»7
                               I  iii L^ UJ |f I  ^J 1,11 ^J uJ uj LU \jt uJ LU LU UJ LU UJ LLJ uj
 O O O O O O O  O O  O  *""  O O O O O O O O O O
lUJLLJUJLLJlULUUJuJLUUJUJLULU
                 UJUJUJUJUJUJUJ^^UJUJUJuJi^UJUJUJUJUJUJUJU
                 fninp^ri^(DK-^f^^fs^inr^^in^or^^rNror^incDrNfOf^fn^^c»irj*nMrNir^^^
                    tD^'-aDCDV'-D^-
                                                                                             r)to^-mLnr^a3*-iftrMti>«o\n'-inrMr^
                  nnnffin(cion«Ba«  S'O'E S S fc»i  2  «  «>  y^  —  £  c
                                         —  01"—" —  w »>f *-' »-" Oi-ixeDiBino5DliiiiS<
-------
TABLE 1   Average Modeled I
! F«posure Concentrations
Chemical
2.3,7,8-TCDD
1,2,3,7,8 PeCDD
1 2,3,4.7,8 HxCDD
1,2,3,6,7,8 HxCDD
1,2,3,7,8,9 HxCDD
1,2.3,4.6.7,8-HpCDD
OCDD
2,3.7,8-TCDF
1,2,3,7.8- PeCDF
2.3,4. 7,8- PeCDF
,2,3,4, 7,8-HxCDF
,2,3.6,7.8-HxCDF
,2,3,7.8,9-HxCDF
2,3,4,6,7, 8-HxCDF
,2,3,4,6,7,8 HpCDF
,2,3.4,7.8,9 HpCDF
OCDF
Tetrachloroblphenyl
Hexachloroblphenyt
Heptachtor oblphenyt
Benzo(a)pyrene
Benzo(b)f1uoranthene
Bl»(2-ethythexyt)phthalate
Carbon tetrachlorlde
Dibenz(a,h)anthracene
Dl(n)octyt phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Nlavg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Leafy
Produce
Cone
mg/kgWW
50E-12
90E-11
1 2E-10
34E 11
39E-11
20E-09
26E-07
74E-11
45E-10
6 1E-10
41E-10
94E-10
2 1E-10
68E-10
22E-09
1 7E-10
5 6E 08
66E 10
1 2E 09
3 8E-08
4 2E-06
20E 06
2 3E-03
36E-07
95E-09
44E-04
20E-09
1 1E-08
1 1E-08
1 9E-10
5 4E-08
95E-09
22E-08
94E-08
7 1E-07
47E-11
4 7E-08
93E-10
1 3E 07
50E-05
5 OE-05
1 6E-08
95E 07
1 4E-07
3 4E 08
36E-06
Root
Produce
Cone
mg/kgV/W
75E-15
38E-14
23E-14
5 7E-14
37E-14
24E-13
1 6E-12
71E-14
20E-13
24E-13
50E-13
4 7E-13
1 1E-13
53E-13
22E 12
29E-13
2 7E-12
1 8E-10
27E-11
1 6E-10
4 BE-11
1 7E-09
46E-11
1 3E-07
79E-10
3 2E-08
16E-11
1 5E-07
4 6E-08
22E-09
1 9E-07
87E-10
84E-12
83E-12
1 3E-10
49E-16
40E-11
25E 14
3 1E-11
4 3E 09
4 3E 09
69E 13
1 9E 10
1 OE-10
6 1E-14
83E-10
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mgl\_
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
1 3E-11
2 2E-10
1 5E-10
39E-11
54E-11
42E-10
7 7E-08
40E-11
1 9E-10
1 1E-09
6 1E-10
1 1E-09
25E-10
73E-10
59E-10
1 2E-10
64E-09
25E-09
i6E-09
50E-08
32E-06
1 9E-06
26E-04
1 1E-10
52E-07
2 9E-04
20E-09
93E-09
1 4E-09
88E-11
21E-05
4 8E-07
22E-09
3 6E-08
1 2E-08
1 7E-11
12E-09
2 1E-09
75E 09
9 3E-08
93E 08
1 5E 08
69E 07
2 8E 08
7 7E 07
1 6E-08
-------
  TABLE 1   Average Modeled Frwirnrimnntnl F'pnvirp ronrrnlrattons
Chemical
	 — -- 	 	
2.3.7.8 TCDD
1.2. 3.7.8- PeCDD
1.2.3,4.7,8 HxCDD
1.2.3.6,7.8 HxCDD
1.2,3.7,8,9 HxCDD
1,2.3,4.6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1.2,3,7,8-PeCDF
2.3,4.7,8-PeCDF
1, 2,3,4, 7,8-HxCDF
1,2,3,6,7,8-HxCDF
1.2,3.7,8,9-HxCDF
2.3,4,6.7.8 HxCDF
1.2,3,4.6,7.8 HpCDF
1,2,3,4,7,8,9-HpCDF
OCDF
TetrachloroNphenyt
Hexachlorobiphenyt
Heptachlorobiphenyt
Benzo(a)pyrene
Benzo(b)f)uoranlhene
Bl«(2-ethyfhexy1)phthalate
Carbon tetrachlorlde
Dib«nz(a,h)anthracene
Dl(n)octyt phlhalate
Heplachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopenladlene
Hexachlorophene
lndeno(1,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea

N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2 avg
N2 avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
1 cm Soil
Cone
mg/kg
47E-11
22E-10
24E-10
4 1E-10
7 RF m
f, Ot_~ 1 \J
30E-09
1 5E-08
43E-10
1 3E-09
16E-09
37E-09
34E-09
8 1C. in
I C 1 U
1 QF OQ
J UC ~\jy
2TC r\a
JC ^JO
30E-O9
45E-08
52E 08
85E06
83E-08
1 1E 06
5 1E-06
40E-07
29E-06
24E-06
1 3E-07
25E-09
47E-06
1 3E-05
2 1E-07
67E-06
28E-06
4 6E-07
1 8E-05
22E-05
47E-08
2 6E-07
1 2E-06
7 BE -05
2 4E-04
2 4E-04
1 8E-O6
3 4E-04
1 6E-06
82E-05
1 2E-05
Beef
Cone
mg/kgWW
2 4E-11
4 IE 10
28E-10
73E-11
1 nc in
1 ut- 1U
8 1E-10
1 5E-07
77E-11
36E-10
2 1E-09
1 1E-09
2 1E-09
4 HP in
OC- 1U
1 4P./K)
i ^c -ira
1 i F no
I 1 C -Uj
22E-10
1 2E-08
53E4)9
34E^39
95E 08
79E-06
46E-06
65E 04
33E 10
9 7E 07
72E-04
5 1E-O9
37E-08
66E-09
41E-10
38E-O5
90E-07
4 1E-09
71E-08
22E-08
38E-11
22E-09
48E-09
1 7E-08
22E07
22E 07
2 9E 08
1 4E 06
52E-08
1 9E 06
3 1E-08
Pork
Cone
mg/kgWW
6 1E-12
78E 11
5 IE 11
19E-11
2 1C 4 4
ZE-1 1
1 5E-10
2 5E 08
1 7E-11
70E-11
39E-10
27E-10
42E-10
O CC 4 1
9 bfc-1 1
1 nc in
j Ufc- 10
27c 1 n
(fc-10
63E 11
2 1E^>9
4 1E 09
25E09
1 8E 08
5 1E-07
36E 07
42E-05
1 3E-10
1 1E 07
46E05
36E-10
3 3E-08
75E-09
46E-10
24E-06
1 1E-07
1 7E 09
2 4E-08
9 8E-08
33E-11
1 OE-10
64E-09
49E 08
73E 07
73E-07
1 3E 07
3 6E-05
1 2E-09
7 9E-06
8 2E-09
Chicken
Cone
mg/kgWW
? 3E 13
IDE 12
52E 13
79E-13
6 5E-13
1 2E 12
' 83E 12
45E-13
1 1E-12
56E 12
95E 12
76E-12
1 BE 12
7 7E 12
1 1E-11
33E 12
98E 12
35E 10
2 IE 10
2 1E-10
23E 11
1 2E 10
1 2E 12
5 7E-13
18E-10
22E 12
70E-14
6 1E-11
14E-11
83E 13
35E-09
19E 10
12E-11
92E-09
37E 11
13E-12
4 1E-10
72E-11
15E-06
1 4E 07
1 4E-07
20E 10
1 2E-06
1 4E-11
1 6E 06
7 1E 09
Egg
Cone
mg/kgWW
TIC 1-1
J 1 C • 1 J
1 4E 12
7 ?E 13
I IE 12
90E 13
16E 12
1 1E-11
63E-13
1 5E-12
7 7E-12
1 3E 11
1 OE-11
25E-12
1 1E-11
1 5E-11
45E-12
1 4E-11
4 BE 10
2 BE 10
29E 10
2 BE 08
1 6E 07
15E09
72E 10
2 3E 07
2 BE 09
B8E-11
7 6E-08
1 BE 08
10E09
44E 06
2 4E-07
1 4E-10
1 2E 08
2 9E-OB
1 5E-12
98E-12
1 2E 10
1 5E 06
1 2E 08
1 2E 08
32E-10
1 2E 06
28E-10
1 6E 06
7 1E-09
Milk
r*r»nr-
^Of 1C
mg/kgvVW
Inr 8
5 OE-09
32E 09
9 OE-08
3 1E-06
1BE^)6
26E-04
14E 10
38E-07
28E^)4
20E-O9
1 5E-O8
27E^)9
1 8E-10
15E-05
35E-07
51E-10
27E^)9
63E-08
43E 14
1 7E-10
1 7E-09
1 8E-08
35E07
3 5E-07
6 2E 09
2 7E 06
4 4E 07
1 2E 07
1 OF 08
Butler
Cone
mg/kgWW

75E-11
1 3E-09
86E-10
2 2E-10
31E-10
25E-09
45E-07
24E-10
1 1E-09
64E-09
35E-09
65E-09
1 5E-09
43E-09
34E-09
6 BE 10
38E-08
1 6E-08
1 1E-08
29E-07
3 1E-06
18E^)6
26E-04
1 4E-10
38E-07
28E44
2 OE-09
1 5E-O8
27E^»
16E-10
1 5E-O5
35E-07
5 IE 10
27E09
6 3E 08
43E 14
1 7E 10
1 7E 09
18E08
35E 07
3 5E 07
6 2E 09
2 7E 06
4 4E 07
1 2E 07
1 OF OR
Exposed
Produce
Cone
mg/kgWW

39E 14
66E 13
91E-13
30E-13
3 IE 13
1 5E-11
19E09
55E-13
33E-12
44E 12
34E 12
7 1E-12
1 6E-12
54E-12
1 9E-11
1 6E-12
4 OE-10
1 OE-11
99E-12
27E 10
3 1E-08
1 5E 08
16E-05
25E07
21E09
3 1E 06
1 4E-11
15E-09
65E09
43E-11
1 2E 08
2 1E-09
24E09
1 3E 08
6 4E 08
83E 12
83E 09
23E 10
1 9E 08
62E 06
6 2E 06
7 3E 09
38E 07
2 1E 08
7 GE 09
1 ?F 06
Protected
Produce
Cone
mg/kgWW

3 IE 15
1 5E-14
33E 15
1 IE 14
3 7E 15
25E 14
27E-13
33E 14
73E-1*
74E-14
1 OE-13
94E-14
2 2E-14
1 1E-13
29E 13
37E 14
1 7E 13
93E 12
2 BE 12
1 4E 12
1 4E 10
5 BE 10
1 OE 11
45E 07
1 5E 10
1 2E-12
26E 13
26E-09
1 1E 08
74E 11
1 3E 10
1 7E 10
27E09
8 7E 09
5 7E 08
2 3E 12
87E09
15E 10
1 8E 08
1 1E 05
1 IE 05
1 IE 08
50E07
3 2E 08
6 5E 10
2 1F 06
Volume V, Appendif
-------
TABLE 1   Average Modeled Fnvimnmental f »pniute Conrrnliatinns
Chemical
2.3,7.8-TCDO
,2,3.7.8-PeCDD
.2,3.4.7,8-HxCDD
. 2,3.6, 7,8-HxCDD
,2,3,7,8.9-HxCDD
,2,3.4.6,7,8-HpCDD
OCDD
2.3.7,8-TCDF
1,2,3,7,8-PeCDF
2,3.4, 7,8-PeCDF
1,2,3,4,7.8-HxCDF
1.2.3.6,7,8-HxCDF
1 2 3,7,8,9-HxCDF
2 3.4,6,7,8-HxCDF
1.2,3,4.6,7.8 HpCDF
1,2,3,4,7,8,9 HpCDF
OCDF
Tetrachlofobiphenyl
Hexachlofobiphenyl
Heptachlorobiphenyl
Benzo(a)pyrene
Benzo(b)fluoranthene
Bls(2-ethylhexyl)phthalale
Carbon tetrachloride
Dibenz(8,h)anthracene
Dl(n)octy) phlhalale
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopenladiene
Hexachlorophene
lndeno( 1 ,2 ,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
7mc
Subarea
N2 avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2 avg
N2 avg
N2 avg
N2 avg
N2 avg
N2avg
N2 avg
N2 avg
N2 avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2 avg
N2 avg
N2avg
N2avg
N2avg
N2 avg
Leafy
Produce
Cone
mg/kgWW
20E-12
35E-11
49E-11
1 3E-11
1 5E-11
8 OE-10
1 OE-07
29E-11
1 8E-10
24E-10
1 6E-10
3 7E-10
84E-11
2 7E-10
8 7E-10
6 7E-11
2 2E 08
2 6E-10
46E-10
1 5E-08
1 7E-06
8 OE-07
9 1E-04
1 4E-07
30E-09
1 7F-04
7 7E-10
43E-09
42E-09
73E-11
1 7E-08
30E-09
69E-09
3 OE-08
2 3E-07
1 5E-11
1 5E-08
3 OE-10
4 2E-08
2 OE-05
2 OE-05
50E-09
3 OE-07
4 5E 08
1 1E-08
1 1E-06
Root
Produce
Cone
mg/kgWW
2 BE 15
1 3E 14
75E-15
1 8E-14
1 2E-14
77E-14
51E-13
2 7E-14
73E-14
83E-14
1 6E-13
15E-13
35E-14
1 7E-13
7 1E-13
9 1E-14
83E-13
69E-11
1 1E-11
6 4E 11
1 7E 11
65E-10
1 6E-11
53E 08
25E-10
1 2E-08
63E-12
6 OE-08
1 BE -08
86E-10
5 8E-08
27E-10
27E-12
26E-12
43E-11
1 6E-16
1 3E-11
79E-15
1 OE-11
1 7E-09
1 7E-09
2 2E-13
6 OE-11
32E-11
1 9E-14
26E-10
River
Fish
Cone
mg/kg
2 4E-12
1 1E-11
62E-12
1 IE 11
68E-12
1 OE-11
95E-13
2 1E-11
7 1E-11
88E-11
94E-11
88E-11
2 1E-11
1 OE-10
7 7E-11
98E-12
30E 12
69E 09
1 3E 07
8 3E 08
1 6E 07
2 BE 06
33E 08
1 3E 08
1 6E 05
1 4E-07
2 2E 08
1 3E-04
92E06
1 1E-08
7 3E-07
2 IE-OS
8 7E-11
8 7E-08
1 6E-08
46E-11
1 4E-07
8 1E-10
4 9E-07
1 7E-04
96E-04
1 5E 08
22E 06
1 6E 10
30E 07
97E07
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
, NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Rivei
Watei
Cone
mg/L
1 4E 16
6 7E 16
5 BE 17
3 IE 16
20E 16
29E-16
57E 15
1 6E-15
30E-15
2 7E-15
2 BE 15
26E 15
6 1E-16
30E-15
45E-15
57E-16
1 1E-15
1 3E-12
2 1E-13
42E-13
28E-12
45E-11
1 7E-12
4 4E-10
1 2E-11
2 3E-12
43E 14
24E-10
29E 10
4 1E-12
1 4E-10
1 4E-11
87E-11
20E 09
40E-09
23E-12
64E-11
50E-11
3 1E-09
4 5E 08
4 5E-08
24E 10
29E 08
3 1E-10
25E-09
2 2E 09
Lake
Waler
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
4 9E 12
85E 11
5 7E-11
1 5E 11
2 IE 11
1 7E-10
30E 08
1 6E-11
74E-11
4 2E-10
23E-10
43E-10
98E-11
28E-10
22E-10
45E 11
25E-09
9BE-10
63E-10
1 9E-08
1 3E-O6
73E-07
1 OE-04
4 4E-11
1 6E^J7
1 1E-04
8 OE-10
36E-09
54E-10
35E-11
6 7E-06
1 5E-07
7 1E-10
1 2E 08
3 8E-09
55E-12
39E-10
67E-10
2 4E 09
3 7E-08
3 7E 08
4 8E 09
22E 07
90E 09
25E 07
50E-09
-------
  TABI E 1   Average- ModplM f rwi.nnmrMl.il r.pnsurp f nnr rnlrnhnns

Chemical

2.3.7.8 TCDD
1.2.3.7.8 PeCDD
1.2.3.4.7,8 H»CDD
1.2.3.6,7,8 HxCDD
1.2.3.7,8.9 HxCDD
1,2,3,4,6.7,8 HpCDD
OCDD
2,3,7,8-TCDF
1.2.3,7.8-PeCDF
2,3,4,7,8-PcCDF
1,2,3,4,7,8-HxCDF
1,2,3,6,7,8-H)(CDF
1.2. 3.7.8,9 HxCDF
2.3,4,6,7,8 HxCDF
1.2.3.4.6.7.8 HpCDF
1, 2,3,4, 7,8.9-HpCDF
OCDF
Tetrachlorobiphenyl
Hexachlorobiphenyl
Heptachlorobiphenyl
B«nzo(a)pyrene
Benzo(b)riuoranthene
Bis(2-ethythexy1)phthalate
Carbon letrachloride
Dlbenz(a,h)anthracene
Di(n)octy1 phlhalale
Heplachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalenl)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc

Subarea

N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
1 cm Soil
Cone
mg/kg
2 1E-11
1 OE-10
1 1E-10
1 9E-10
1 2E 10
1 4E-09
69E^>9
1 9E-10
6 OE-10
74E-10
1 7E-09
1 6E-09
3 BE 10
1 BE 09
1 1E-08
1 4E-09
2 1E-08
2 3E 08
3 7E-08
36E 08
5 1E 07
2 2E-06
1 8E-07
1 3E-06
1 2E-06
5 5E-08
1 1E-09
2 1E-06
57E-06
9 3E-08
31E-06
1 3E-06
24E-07
94E-06
1 2E-05
25E-08
1 4E4)7
6 5E 07
4 1E-05
1 1E-04
1 1E-04
9 5E-07
1 BE 04
8 7E-07
4 4E-05
62E06
Beef
Cone
mg/kgWW
1 IE 11
1 BE-10
1 2E 10
32E 11
44E 11
35E-10
64E 08
33E 11
1 6E-10
9 OE-10
50E-10
92E-10
21E-10
6 1E-10
48E-10
9 7E-11
53E 09
2 3E 09
1 5E 09
4 IE 08
34E 06
20E 06
2 BE 04
1 4E-10
4 5E-07
31E04
22E-09
1 6E 08
29E-09
1 8E-10
18E-05
4 2E-07
2 1E 09
3 7E-08
1 1E-08
20E-11
1 1E 09
2 5E-09
89E 09
97E 08
9 7E 08
1 5E-08
74E07
2 7E-08
99E-07
1 6E-08
Pork
Cone
mg'kgWW
2 71 1?
34E 11
22E 11
84E 12
99E 12
64E 11
1 IE 08
75E-12
3 1E-11
1 7E-10
12E-10
18E-10
42E-11
1 3E-10
1 2E-10
29E-11
93E-10
1 8E-09
1 1E-09
78E-09
22E-07
1 6E-07
1 8E-05
57E-11
53E-08
2 OE-05
1 6E-10
1 4E-08
33E09
2 OE-10
1 1E-06
54E 08
89E-10
1 3E 08
5 1E-08
1 7E-11
52E-11
34E 09
26E-08
32E-07
32E-07
69E-08
1 9E 05
6 1E-10
4 2E 06
4 3E 09
Ohrrt
-------
TABLE 1   Average Moclrlrd Frwirnrmipnlal Frposute Concenltations
Chemical
2.3,7,8-TCDD
1.2.3,7.8-PeCDD
1,2,3.4, 7.8-HxCDD
1,2.3.6,7.8-HxCDD
1. 2,3,7,8.9 HxCDD
1,2,3,4,6.7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2.3,7,8-PeCDF
2.3,4, 7,8-PeCDF
1.2,3.4, 7.8-HxCDF
1,2.3.6.7.8-HxCDF
1,2,3.7,8.9-HxCDF
2 3,4 6,7.8-HxCDF
1 2,3 A 6.7.8 HpCDF
1,2,3,4, 7.8,9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachlotoblphenyl
HepJachtoroblphenyl
Benzo(a)pyrene
Benzo(b)nuoranthene
Bi«(2-ethylhexyt)phthalate
Carbon letrachlorlde
Dibenz(a,h)anthracene
Dl(n)octyl phthalate
Meplachlor
Hexachlofobenzene
Hexachlorobutadiene
Hexachtorocyctopentadiene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
Lealy
Produce
Cone
mg/kgWW
85E-13
1 5E-11
2 1E-11
58E-12
66E-12
35E-10
4 5E-08
1 3E-11
7 7E-11
1 OE-10
70E-11
1 6E-10
37E-11
1 2E-10
38E-10
29E-11
96E-09
1 1E-10
2 OE-10
65E-09
72E-07
35E-07
40E-04
62E-08
1 4E-09
76E-05
3 3E-10
19E-09
18E-09
32E-11
80E-09
1 4E-09
36E-09
1 6E-08
1 2E-07
78E-12
79E-09
16E-10
2 2E-08
86E-06
8 6E-06
26E-09
1 6E-07
2 3E-08
56E-09
6 OE-07
Root
Produce
Cone
mg/kgWW
1 2E-15
60E-15
35E-15
85E-15
54E-15
36E-14
24E-13
1 2E-14
33E 14
37E-14
75E-14
70E-14
1 6E-14
80E-14
33E 13
4 3E-14
39E-13
30E 11
47E-12
2 BE 11
76E-12
28E-10
7 1E-12
2 3E-08
1 2E-10
55E-09
28E-12
26E-08
79E-O9
38E-10
27E-08
1 3E-10
14E-12
1 4E-12
22E-11
82E-17
68E-12
4 1E-15
53E-12
74E-10
74E-10
1 2E-13
31E-11
1 7E 11
1 OE-14
1 4E-10
River
Fish
Cone
mgfkg
. NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg'kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
lake
Water
Cone
mg(L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg'kgWW
2 2E-12
3 7E-11
25E-11
6 5E-12
r^
9 1E-T2
73E-11
1 3E-08
68E-12
32E-11
1 8E-10
1 OE-10
1 9E-10
4 3E-11
1 2E-10
98E-11
20E-11
1 1E-09
43E-10
?8E-10
85E-09
5 5E-07
3 2E-07
45E-05
1 9E-11
7 7E-08
50E-05
35E-10
16E-09
2 4E-10
15E-11
31E-06
71E-08
37E-10
60E-09
19E-09
2 9E-12
2 OE-10
35E-10
1 2E-09
1 6E 08
1 6E-08
2 5E-09
1 2E 07
4 7E 09
1 3E-07
26E-09
 Volume V, Appendix V-11
-------
  TABIE 1   Aveiagp Mociplpd Fnvifonnipnlal r.pnsu
Chemical
2,3.7.8 TCDD
1.2,3,7,8-PeCDD
1,2.3.4.7,8 HxCDD
1,2.3.6,7.8 HxCDD
1.2.3,7,8.9 HxCDD
1,2,3,4,6,7,8 HpCDD
OCDD
2,3.7.8-TCDF
1,2.3.7,8-PeCDF
2.3,4, 7.8-PeCDF
1,2.3.4,7,8-HxCDF
1,2,3,6,7,8-HxCDF
1,2,3.7,8.9-HxCDF
2.3.4.6.7.8-HxCDF
1.2.3.4.6.7.8 HpCDF
1,2,3,4,7.8,9 HpCDF
OCDF
Tetrachloroblphenyl
Hexachlorobiphenyl
Heptachloroblphenyl
Ben2o(a)pyrene
Benzo(b)rTuoranthene
Bis(2-«thy1hexy1)phlhalate
Carbon telrachlorlde
Dlbenz(a,h)anthracene
Dl(n)octyl phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno(1,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalenl)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
S1 avg
SI avg
SI avg
SI avg
SI avg
SI avg
S1 avg
SI avg
S1 avg
SI avg
SI avg
SI avg
SI avg
SI avg
S 1 avg
S 1 ava
SI avg
SI avg
SI avg
SI avg
S1 avg
SI avg
SI avg
S1 avg
SI avg
SI avg
S1 avg
S1 avg
S1 avg
S1 avg
SI avg
S1 avg
S1 avg
S1 avg
S1 avg
S1 avg
SI avg
S1 avg
SI avg
S1 avg
S1 avg
SI avg
SI avg
SI avg
SI avg
S1 avg
1 cm Soil
Cone
mg/kg
1 2E-10
54E-10
55E-10
95E-10
61E 10
69E-09
1 1E-09
33E-09
39E-09
B5E-09
8 OE-09
19E09
9 1E-09
5 4E-08
fi QF no
u :yc Uj
1 OE-07
1 3E-07
2 2E-07
2 1E-07
2 7E-06
1 3E-05
95E 07
75E-06
56E-06
3 2E-07
63E-09
1 2E-05
33E-05
5 4E-07
1 5E-05
63E 06
1 1E-06
42E-05
52E-05
t 1E-07
6 2E-07
29E-06
1 9E-04
6 2E-04
6 2E 04
4 3E-06
8 OE-04
39E 06
2 OE-04
28E-05
Beel
Cone
mg/kgWW
62E-11
1 OE-09
7 1E-10
1 BE 10
26E-10
2 1E 09
3 7E-07
1 9E-10
9 1E-10
52E-09
29E-09
1 2E 09
7 flP fKJ
< oc-uy
c ep m
3 JC • 1 U
3 1E-08
1 3E 08
8 7E 09
24E 07
2 OE 05
1 2E 05
1 7E-03
84E-10
22E 06
1 8E-03
1 3E-08
9 3E-08
1 7E-08
10E09
8 8E-05
2 1E-06
97E-09
1 7E-07
5 2E-08
9 1E-11
52E-09
1 2E-08
4 1E08
57E-07
57E-07
70E 08
34E 06
1 2E 07
4 5E 06
75E 08
Pork
Cone
mg/kgWW
1 5E 11
20E 10
1 3E-10
46E 11
55E-11
37E-10
63E-08 '
43E-11
18E-10
1 OE-09
66E 10
1 nc no
1 Ut-U9
24E-10
74E-10
c cc 1 n
O DC- 10
Ice i n
be- 10
54E09
1 OE 08
64E 09
46E 08
1 3E 06
93E 07
1 1E 04
33E-10
25E-07
1 2E 04
93E 10
8 4E-08
1 9E-08
1 2E-09
54E06
2 6E-07
4 OE 09
5 7E-08
2 3E-07
78E-11
24E-10
1 5E-08
1 2E 07
1 9E 06
19E-06
3 1E-07
8 5E-05
28E-09
1 9E-05
1 9E-08
Chickrn
Cone
mg/kgWW
5 7E 13
25E 12
1 2E 12
1 BE 12
1 5E 12
27E 12
1 9E 11
1 IE 12
2 7E 12
1 4E 11
22E-11
1 8E-1 1
42E 12
1 BE 11
2 4E-1 1
7 5E 12
22E 11
89E 10
53E-10
54E 10
55E 11
32E 10
29E-12
15E 12
42E-10
56E 12
18E 13
1 5E 10
37E-11
2 1E 12
80E09
43E 10
29E-11
2 2E 08
8 7E-11
30E 12
98E-10
1 7E-10
36E06
35E 07
35E 07
4 7E-10
2 7E 06
33E-11
3 7E 06
1 7E 08
Egg
Cone
mg/kgWW
7 8E 13
34E 12
1 7E 12
25E 12
2 1E 12
3 BE 12
26E-11
16E 12
37E-12
1 9E-11
30E-11
2 4E-11
5 BE 12
25E 11
3 4E-11
1 OE-11
3 1E-11
1 2E 09
73E-10
74E 10
69E-08
4 OE-07
36E-09
1 BE 09
52E07
70E 09
22E-10
1 9E 07
4 6E 08
27E09
1 OE 05
54E07
34E 10
2 BE 08
69E08
35E-12
23E-11
28E-10
36E 06
30E 08
30E 08
77E 10
2 7E-06
65E-10
3 7E 06
1 7E 08
Milk
Cone
mg/kgWW
47 f 1 •>
' C - 1 £
79E 11
5 3E 11
1 4E 11
1 9E-11
1 5E-10
2 BE 08
15E 11
69E-11
40E 10
22E-10
40E-10
92E 11
26E-10
2 1E 10
4 1E-11
1 OE 09
66E-10
1BE-08
79E-06
46E-06
8 5E-04
37E-10
8BE-07
7 2E-04
51E-09
37E-08
68E-09
42E-10
35E05
8 2E-07
12E09
64E-09
1 5E-07
1 OE-13
41E 10
40E 09
43E 08
90E 07
90E 07
1 5E 08
64E 06
1 OE-06
29E 07
24E-08
Cheese
Cone
mg/kgWW
7nr- t «
OE 1 1
1 2E 09
80E-10
2 IE 10
29E 10
23E-09
4 2E-07
22E-10
IDE -09
59E-09
32E-09
6 OE-09
14E-09
4 OE-09
31E-09
62E-10
35E-08
15E-08
99E09
27E-07
79E-06
46E-06
8 5E-04
37E-10
88E-07
72E-04
51E-09
3 7E-08
68E-09
42E-10
35E-05
8 2E-07
12E-09
64E-09
1 5E-07
1 OE-13
41E-10
4 OE-09
4 3E 08
90E 07
90E 07
1 5E 08
64E 06
1 OE-06
29E 07
24E 08
Milk
Desseit
Cone
mg/kgWW

30E-11
5 1E 10
35E-10
90E-11
1 3E-10
1 OE 09
1 8E-07
96E-11
45E-10
26E-09
14E-09
26E-09
59E-10
1 7E-09
1 4E-09
27E-10
1 5E-08
66E 09
43E-09
12E-07
79E-06
46E-06
65E-04
37E-10
8 BE 07
7 2E-04
51E-09
3 7E-08
68E-09
42E-10
35E-05
82E-07
1 2E-09
64E-09
1 5E-07
1 OE-13
4 1E-10
4 OE-09
4 3E-08
90E 07
9 OE-07
1 5E-08
6 4E-06
1 OE 06
29E 07
24E-08
Yogurt
Cone
mg/kgVWV

4 7E 12
79E-11
53E-11
1 4E 11
1 9E-11
15E-10
2 8E-08
15E-11
69E-11
40E-10
22E 10
40E-10
92E-11
26E-10
2 IE 10
4 1E-11
23E-09
1 OE-09
66E-10
1BE-08
79E06
46E-06
6 5E-04
37E-10
8 8E-07
72E-04
5 1E-09
3 7E 08
68E-09
42E-10
3 5E-05
82E-07
1 2E 09
64E-09
1 5E-07
1 OE-13
4 IE 10
4 OE 09
4 3E 08
90E 07
90E 07
1 5E 08
64E 06
1 OE 06
29E 07
24E 08
Cream
Cone
mg/kgWW

58E 11
99E 10
66E-10
1 7E-10
2 4E-10
1 9E-09
3 5E-07
1 8E-10
86E-10
49E-09
27E-09
50E 09
1 1E-09
33E-09
26E-09
52E-10
2 9E 08
1 3E-08
82E09
2 3E-07
79E-06
46E-08
6 5E-04
37E-10
8 BE 07
7 2E-04
5 1E-09
3 7E-OB
68E-09
42E-10
35E-05
82E-07
1 2E 09
64E09
1 5E 07
1 OE-13
4 1E 10
40E-O9
43E 08
90E 07
90E 07
1 5E 08
64E 06
1 OE 06
2 9E 07
2 4E 08
Butler
Cone
mg/kgWW

1 9E 10
32E-09
22E09
5 7E-10
79E-10
63E-09
12E-06
60E-10
28E-09
1 6E-08
89E-09
1 6E-08
3 BE -09
1 1E-08
85E09
1 7E-09
96E-O8
42E-08
2 7E-08
75E-07
79E-06
46E-06
6 5E 04
37E-10
8 8E-07
7 2E-04
3 7E-08
68E-09
42E-10
35E-05
8 2E 07
12E09
64E09
1 5E 07
10E 13
4 1E 10
40E09
4 3E 08
90E 07
90E 07
1 5E 08
6 4E 06
1 OE 06
2 9E 07
2 4F 08
Exposed
Produce
Cone
mg/kgWW

9 BE 14
1 7E-12
23E 12
76E-13
79E-13
38E-11
47E09
1 4E 12
83E-12
1 1E-11
86E-12
8E-11
1E-12
4E 11
7E-11
1E-12
1 OE-O9
26E 11
25E 11
69E-10
7 9E 08
3 BE -08
42E05
65E-07
48E-09
79E-06
36E-11
39E09
1 7E 08
1 IE 10
2 7E 08
49E-09
57E09
3 1E 08
1 5E 07
20E 11
20E 08
56E 10
46E 08
1 6E 05
1 6E 05
1 7F 08
9 OE 07
50E 08
1 RF nn
i or uo
29F 06
Protected
Produce
Cone
mg/kgWW

78E 15
36E 14
7 BE 15
26E 14
86E-15
57E-14
61E-13
B4E-14
1 BE -13
18E-13
23E-13
22E-13
5 IE 14
25E-13
66E-13
84E 14
38E-13
24E-11
7 IE 12
35E 12
35E-10
15E09
25E 11
1 IE 06
33E 10
3 IE 12
66E 13
65E09
2 9E 08
19E 10
30E-10
40E-10
63E 09
2 1E 08
1 3E 07
53E-12
2 IE 08
35E 10
4 3E 08
2 7E 05
2 7E 05
26E 08
i jf nc
1 £ C \J\J
75E08
5 OF 06
Volume V, Appends   V
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                                                                                                                                       i S S  2  to
-------
 TABLE  1   Average Modolrr) Frwirnnmrrital FirpOMJfr Coiirrnlralinns
Chemical
2.3.7,8-TCDD
1.2,3.7,8 PeCDD
1.2,3.4,7,8 HxCDD
1.2,3.6,7.8 HxCDD
1.2.3.7,8.9 HxCDD
1,2,3.4.6,7,8-HpCDD
OCDD
2,3.7,8-TCDF
1,2.3,7.8-PeCDF
2,3,4.7,8-PeCDF
1,2,3,4,7,8-HxCDF
1.2,3,6,7,8-HxCDF
1.2,3,7,8,9-HxCDF
2.3,4.6.7,8-HxCDF
1, 2.3,4.6.7.8- HpCDF
1,2.3,4,7,8.9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachlofobiphenyl
Heplachloroblphenyl
Benio(a)pyr«ne
Benzo(b)fluoranlhene
Bis(2 -*thy1hexy1)phlhalate
Carbon telrachloride
Dibenz(a.h)anthracene
Dl(n)octyt phlhalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno( 1 ,2.3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
Leafy
Produce
Cone
mg/kgWW
1 OE-12
19E-11
2 6E 11
7 OE-12
8 OE-12
42E-10
5 4E 08
15E-11
93E-11
1 3E-10
85E-11
1 9E-10
4 4E-11
1 4E-10
46E-10
35E-11
1 2E 08
1 4E-10
25E 10
79E-09
8 7E-07
4 2E 07
48E-04
7 4E-08
85E-10
9 IE-OS
40E-10
23E-09
22E-09
39E-11
49E-09
85E-10
20E-09
86E-09
6 5E-08
44E-12
4 3E-09
88E-11
1 2E 08
1 OE-05
1 OE-05
1 4E-09
8 8E-08
1 3E-08
32E09
32E-07
Root
Produce
Cone
mg/kgWW
1 3E-15
52E 15
2 4E-15
5 3E-15
33E-15
22E-14
1 4E-13
1 3E-14
32E-14
34E-14
50E-14
4 7E-14
1 2E-14
53E 14
2 IE 13
26E 14
23E-13
36E-11
57E 12
34E-11
70E 12
34E 10
59E-12
2 BE -08
67E-11
66E-09
33E-12
32E-08
96E-09
46E-10
1 6E-08
74E-11
75E-13
74E-13
1 2E-11
44E-17
36E-12
22E-15
28E-12
90E-10
90E-10
62E 14
1 7E-11
90E-12
55E 15
74E-11
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
lake
Fish
Cone
mg/kg
1 4E-12
55E-12
2 2E-12
3 7E-12
23E-12
33E-12
3 1E-13
1 3E-11
3 7E-11
42E-11
34E-11
3 2E-11
80E 12
J 7E-11
2 7E-11
33E-12
95E-13
1 OE 08
80E-08
58E08
1 OE 07
25E-06
35E-08
28E 08
79E-06
2 8E-07
40E-08
2 7E-04
19E05
22E-08
96E07
1 OE-05
1 1E-10
1 OE-07
20E-08
51E-11
2 8E-07
B9E-10
54E 07
36E 04
2 1E 03
1 8E 08
26E-06
20E-10
30E07
1 3E-06
Rivor
Water
Cone
mg'L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
80E-17
33E 16
2 1E-17
1 1E-16
68E 17
96E-17
1 8E-15
98E-16
1 5E-15
1 3E-15
1 OE-15
96E-16
2 4E-16
1 1E-15
1 6E-15
1 9E-16
35E-16
1 9E-12
1 3E-13
29E-13
1 BE-12
38E-11
1 8E-12
94E-10
58E-12
45E-12
80E-14
50E-10
60E-10
86E-12
1 9E-10
66E-12
1 1E-10
24E-09
51E-09
26E-12
1 3E-10
55E-11
34E-09
9 6E-08
9 6E-08
29E-10
34E-08
4 1E-10
25E-09
3 OE-09
Deer
Cone
mg/kgWW
26E-12
4 4£ 11
1 nF 1 1
J UC 1 1
7 4F 19
* HC \^
1 iE-n
8 7E-11
1 6E-08
82E-12
39E-11
22E-10
1 2E-10
2 2E-10
5 1E-11
1 5E-10
1 1E-10
22E-11
1 3E-09
5 1E-10
3 3E-10
10E-08
6 5E-07
3 9E-07
55E-05
23E-11
4 7E-08
6 OE-05
42E-10
19E-09
29E-10
1 8E-11
19E-06
4 3E-08
2 1E-10
3 5E-09
1 1E-09
1 6E-12
1 2E-10
20E-10
71E-10
1 9E 08
1 9E-08
1 4E 09
66E 08
26E 09
7 3E-08
1 5E 09
Volume V, Appendix/'
-------
TABLE 1   Average Modrli'd f nvimnmrnlal F«po>;iirp ronrrnlralinni
Chemical
2.3,7.8-TCDD
1,2.3,7.8-PeCDD
1,2.3.4.7.8 HxCDD
1.2.3.6,7.8 HxCDD
1,2.3,7,8.9 HxCDD
1,2.3,4,6.7,8 HpCDD
OCDD
2,3,7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4,7,8-PcCDF
1,2.3.4,7.8-HxCDF
1,2.3,6,7.8 HxCDF
1,2.3,7,8,9 HxCDF
2,3,4.6,7.8 HxCDF
1,2,3.4,6.7.8 HpCDF
1, 2,3,4, 7.8,9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachlorobiphenyt
Heptachtoroblphenyt
Benzo(B)pyrene
Benzo(b)fluoranthene
Bl«(2-ethylhexyt)phthalate
Carbon tetrachloride
Dibenz(«,h)antnracene
D)(n)octy1 phlhalale
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
lndeno(1.2.3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalenl)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
7mc
Subarea
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
Wl avg
W1 avg
W1 avg
W1 avg
Wl avg
W1 avg
W1 avg
Wl avg
Wl avg
Wt avg
Wt avg
Wl avg
W1 avg
W1 avg
Wl avg
W1 avg
Wl avg
W1 avg
W1 avg
W1 avg
Wl avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
Wl avg
W1 avg
W1 avg
W1 avg
W1 avg
1 cm Soil
Cone
mg/kg
1 7E 10
78E-10
80E-10
1 4E-09
89E-10
1 OE-08
49E-08
16E-09
48E-09
57E-09
1 2E-08
1 2E-08
28E-09
1 3E-08
79E-08
1 OE-08
1 5E-07
1 9E-07
3 1E-07
3 OE-07
40E-06
1 8E-O5
1 4EO6
1 1E-05
8 1E-06
4 6E-07
90E-09
1 7E-05
47E-05
7 7E-07
22E-05
92E-06
15E-06
58E-05
71E-05
1 5E-07
8 5E-07
40E-06
2 5E-04
8 8E-04
8 BE 04
59E-06
1 1E-03
53E-06
2 7E-04
38E-05
Beef
Cone
mg/kgWW
88E-11
1 5E 09
1 OE 09
26E-10
37E-10
29E-09
53E-07
28E-10
1 3E-09
75E-09
4 1E-09
76E 09
1 7E 09
5 OE-09
39E 09
79E-10
44E 08
1 9E 08
1 2E 08
35E 07
29E 05
1 7E-05
2 4E 03
1 2E 09
32E 06
2 6E 03
1 BE 08
1 3E-07
24E 08
15E-09
1 3E-04
30E-06
1 3E-08
2 3E-07
70E 08
1 2E-10
7 1E-09
1 6E 08
56E-08
8 IE 07
81E07
9 5E-08
46E-06
- 1 7E 07
62E-06
1 OE 07
Pork
Cone
mg/kgWW
22E 11
2 BE 10
1 BE 10
66E 11
79E-11
52E-10
9 OE-08
62E-11
25E-10
1 4E-09
96E-10
1 5E-09
34E 10
1 1E 09
96E-10
22E 10
7 7E 09
1 5E 08
92E 09
65E 08
1 9E 06
1 3E 06
1 5E 04
4 7E 10
37E07
1 7E-04
1 3E-09
1 2E-07
2 7E-08
1 7E-09
79E-06
38E-07
55E-09
7 8E-08
32E-07
1 1E-10
32E-10
2 1E 08
1 6E 07
2 7E 06
27E06
42E07
1 2E 04
38E-09
26E-05
2 7E 08
Chicken
Cone
mg/kgWW
8 1E 13
36E 12
1 BE 12
2 7E 12
22E 12
> 40E-12
2 BE 11
1 6E 12
39E 12
20E-11
32E-11
26E-11
6 1E-12
26E-11
36E-11
1 1E-11
33E-11
1 3E-09
75E-10
7 7E-10
79E-11
45E-10
42E-12
21E-12
6 IE 10
80E-12
25E-13
22E-10
52E-11
30E-12
1 2E-08
63E-10
40E-11
3 OE-08
1 2E-10
4 1E-12
1 3E-09
24E-10
50E-06
5 OE-07
5 OE-07
65E-10
3 7E-06
45E-11
5 1E-06
2 3E-08
Egg
Cone
mg/kgWW
1 1E 12
50E-12
25E-12
3 7E-12
30E-12
55E-12
38E-11
23E-12
53E-12
2 7E-11
4 4E-11
36E-11
8 4E-12
36E-11
49E-11
1 5E-11
45E-11
1 8E-09
1 OE-09
1 1EO9
99E-08
57E-07
52E-09
26E-09
7 7E-07
1 OE-08
32E-10
2 8E-07
66E-08
38E-09
1 5E-05
7 9E-07
4 7E-10
3 9E-08
9 5E-08
48E-12
32E-11
38E-10
50E-06
4 2E-08
4 2E-08
1 1E-09
3 7E-06
90E-10
5 1E-06
2 3E-08
Milk
Cone
mg/kgWW
6 7E-12
1 IE 10
76E-11
20E-11
2 BE 11
2 2E-10
4 OE-08
2 1E-11
98E-11
57E-10
3 1E-10
5 7E-10
1 3E-10
38E-10
30E-10
59E-11
33E-09
1 5E-09
94E-10
2 6E-OB
1 1E^»
66E 06
9 3E-04
52E-10
1 3E-06
1 OE 03
72E-09
5 3E-08
97E-09
60E-10
5 OE 05
1 2E-06
1 7E-09
B6E-09
2 OE-07
1 4E-13
56E-10
54E-09
58E-08
1 3E-06
1 3E 06
2 OE-08
8 7E-06
1 4E-06
39E-07
3 3E-08
Cheese
Cone
mg/kgWW
1 OE-10
1 7E-09
1 IE -09
30E-10
4 1E-10
33E-09
6 OE-07
32E-10
15E-09
8 5E-09
46E-09
B6E-09
2 OE-09
57E-09
45E-09
89E-10
5 OE-08
22E-08
1 4E-08
3 9E 07
1 1E-05
66E-06
93E-04
52E-10
1 3E-08
1 OE-03
72E-09
53E-08
97E-O9
6 OE-10
50E-05
1 2E-06
1 7E-09
86E-09
2 OE-07
14E-13
56E-10
54E09
5 BE -08
1 3E-06
1 3E-06
2 OE-08
8 7E-06
1 4E-06
3 9E-07
3 3E-08
Milk
Dessert
Cone
mg/kgWW
4 3E-11
7 3E-10
49E-10
1 3E-10
1 BE 10
1 4E-09
26E-07
1 4E-10
64E 10
37E-09
2 OE-09
37E-09
85E-10
25E-09
1 9E-09
39E-10
22E-08
95E-09
6 1E-09
1 7E-07
1 1E-05
66E-06
9 3E-04
52E-10
13E-06
1 OE-03
72E-09
53E-O8
97E-09
6 OE-10
50E-O5
1 2E-06
1 7E-09
86E-09
2 OE-07
14E-13
56E-10
54E-09
5 BE 08
1 3E-06
1 3E-06
2 OE-08
8 7E-06
1 4E-06
39E 07
3 3E-08
Yogurt
Cone
mg/kgWW
6 7E-12
1 IE 10
7 6E-11
20E-11
28E-11
2 2E-10
4 OE-08
2 IE 11
98E-11
57E-10
3 1E-10
57E-10
1 3E-10
38E-10
3 OE-10
59E-11
33E-O9
15E-09
94E-10
2 6E-08
1 1E-05
66E-06
93E-04
52E-10
1 3EO6
1 OE-03
72E-09
53E-08
97E^»
6 OE-10
50E-05
1 2E-08
1 7E-09
86E-09
2 OE-07
14E-13
56E-10
54E-09
5 BE 08
1 3E-06
1 3E 06
2 OE-08
8 7E-06
1 4E 06
39E 07
33F 08
Cream
Cone
mg/kgWW
83E-11
1 4E-09
95E-10
2 5E-10
34E-10
2 8E-09
5 OE-07
26E-10
1 2E 09
7 1E-09
39E-09
72E-09
1 6E 09
47E-09
37E-09
74E-10
4 2E 08
1 BE 08
1 2E-08
3 3E-07
1 1E-O5
66E-O6
93E-04
52E-10
1 3E^)6
1 OE-03
72E-09
5 3E-08
97E-09
6 OE-10
50E-05
12E-06
1 7E-09
86EO9
2 OE-07
1 4E-13
56E-10
54E-09
5 BE -08
1 3E-06
1 3E 06
2 OE 08
8 7E 06
1 4E 06
3 9E 07
T IF 08
Butler
Cone
mg/kgWW
2 7E-10
46E-09
3 IE -09
8 1E-10
1 IE 09
9 IE -09
1 7E-08
86E-10
4 OE-09
2 3E-08
1 3E-08
2 4E-OB
54E-09
1 6E-08
1 2E-08
24E^)9
1 4E-07
6 OE-08
39E-08
1 1E-06
1 IE-OS
66E-08
93E-04
52E-10
13E06
1 OE-03
72E-09
5 3E-08
97E-09
6 OE-10
50E-05
1 2E-06
1 7E 09
86E-09
2 OE-07
1 4E-13
56E-10
54E-09
5 BE 08
1 3E 06
1 3E 06
20E 08
8 7E 06
1 4F 06
.3 9F 07
3 IF 08
Exposed
Produce
Cone
mg/kgWW
1 4E-13
24E-12
33E-12
1 1E-12
1 1E-12
54E-11
67E-09
20E-12
1 2E-11
1 6E-11
1 2E-11
26E-11
58E-12
1 9E-11
68E-11
58E-12
1 5E-09
37E-11
36E-11
98E-10
1 1E-07
54E-08
59EO5
92E-07
69E-09
1 IE-OS
5 1E-11
55E-09
24E-08
1 6E-10
39E-08
7 OE-09
78E-09
42E-08
2 IE 07
2 7E-11
2 7E 08
76E 10
6 3E 08
2 IE 05
2 IE 05
2 4E 08
1 2E 06
69E 08
2 5E 08
19F 06
Protccled
Produce
Cone
mg/kgWW
1 1E-14
5 IE 14
1 1E-14
38E 14
1 3E-14
83E-14
89E-1?
1 2E it
26E-13
26E-13
34E-13
32E-13
75E-14
36E-13
96E-13
12E-13
55E-13
34E-11
1 OE-li
50E-12
5 OE-10
2 IE 09
36E-11
1 6E-06
48E-10
44E-12
94E 13
93E-09
4 2E-08
27E-10
44E 10
58E-10
B6E 09
28E 08
1 BE 07
73E-12
2 BE 08
48E-10
5 BE 08
39E 05
39E 05
36E 08
1 6E 06
1 OE 07
2 IE 09
68F 06
-------
TABLE 1   Average Modeled Environmental Fiposure CoiKenli
-------
TABl F 1   Avoragr ModHrd Fnvironmrnln! F»po«uirr Conr rnlrnhmis
Chemical
2,3.7.8-TCDD
1.2.3,7,8-PeCDD
1, 2,3.4, 7,8-HxCDD
1,2,3.6,7,8 HxCDD
1 2 3,7.8,9-HxCDD
1,2,3,4,6,7,8 HpCDO
OCDD
2,3,7.8-TCDF
1,2,3,7,8-PeCDF
2,3,4,7.8 PeCDF
1,2,3,4, 7,8-HxCDF
1.2,3,6,7,8-HxCDF
1,2,3,7,8,9-HxCDF
2.3.4.6.7,8-HxCDF
1,2.3,4.6.7,8-HpCDF
1,2,3.4,7.8.9 HpCDF
OCDF
Teltachloroblphenyl
Hexachlorobiphenyt
Heplachlofobiphenyt
Benzo(a)pyrene
Benzo(b)riuoranthene
Bi»(2-e(hythexy<)phlhalate
Carbon letrachloride
Dlbenz(a,h)anthracene
Dl(n)octy) phlhalate
Meptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
Indenof 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subatea
W2 avg
W2 avg
W2avg
W2 avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2 avg
W2 avg
W2avg
W2 avg
W2 avg
W2 avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2rvg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 avg
W2avg
W2 avg
W2 avg
1 cm Soil
Cone
mg/kg
75E-11
3 1E-10
28E-10
46E-10
29E-10
33E-09
1 5E-08
72E-10
20E-O9
23E-09
42E-09
40E-09
98E-10
45E-09
2 6E 08
33E-09
4 7E-08
9 OE-08
1 5E-07
1 5E-07
1 6E 06
88E 06
5 3E-07
5 1E 06
26E-06
2 2E-07
43E-09
83E-06
23E-05
3 7E-07
70E-06
29E-06
4 BE-07
1 8E-05
2 3E-05
4 9E-08
2 7E-07
1 3E-06
8 1E-05
42E-04
4 2E-04
1 SE-06
3 5E-04
1 7E-06
86E 05
1 2E-05
Beel
Cone
mg/kgWW
4 2E 11
71E 10
48E-10
1 2E-10
1 7E-10
14E-09
2 6E-07
1 3E-10
62E-10
36E-09
1 9E-09
36E-09
82E-10
24E-09
1 BE 09
36E-10
2 1E-08
9 1E-09
60E-09
1 7E-07
1 4E-05
8 1E-06
1 1E-03
58E-10
1 OE-06
1 3E-03
B8E-09
6 4E-08
1 2E-08
71E-10
4 1E-05
9 5E-07
43E-09
7 6E-08
2 3E 08
4 1E-11
23E-09
51E-09
1 8E-08
39E-07
39E-07
3 1E-08
1 5E-06
55E 08
20E 06
3 3E-08
Pork
Cone
mg/kgWW
1 OE 11
1 3E-10
86E-11
2 7E-11
3 4E-11
25E-10
4 3E-08
29E-11
12E-10
67E-10
4 1E-10
68E-10
1 6E-10
4 7E-10
40E 10
89E-11
36E-09
7 1E-09
4 4E-09
3 1E 08
8 9E-07
64E-07
7 4E-05
23E-10
1 2E-07
8 1E-05
64E-10
5 8E-08
1 3E-08
80E-10
25E-06
1 2E-07
1 8E-09
2 5E-08
1 OE-07
34E-11
1 1E-10
67E-09
5 1E 08
1 3E-06
1 3E-06
1 4E-07
3 7E 05
1 2E 09
83E-06
8 5E-09
Chicken
Cone
mg/kgWW
36E 13
1 4E 12
6 IE 13
8 8E 13
7 OE-13
1 3E 12
8 BE 12
75E 13
16E-12
79E 12
1 1E-11
8 BE 12
22E 12
89E-12
1 2E 11
36E-12
1 OE 11
6 1E 10
36E-10
37E 10
33E-11
2 2E 10
1 6E-12
10E-12
1 9E 10
38E 12
1 2E-13
1 1E 10
25E 11
1 5E-12
37E-09
20E 10
1 3E 11
96E 09
38E-11
1 3E-12
43E-10
76E-11
1 6E 06
2 4E 07
2 4E 07
2 1E 10
1 2E-06
1 4E 11
1 6E 06
74E 09
Egg
Cone
mg/kgWW
50E 13
20E 12
85E-13
1 2E-12
9 7E-13
1 8E-12
1 2E-11
10E-12
2 3E-12
1 1E-11
15E-11
1 2E-11
30E-12
1 2E-11
1 6E-11
49E-12
1 4E-11
84E-10
50E-10
5 1E-10
4 1E-08
2 7E-07
20E 09
1 3E-09
2 4E-07
4 8E-09
1 5E-10
1 3E 07
32E08
1 BE -09
46E-06
2 5E-07
1 5E-10
1 2E-08
3 OE-08
15E-12
1 OE-11
1 2E-10
1 6E 06
2 OE-08
2 OE-08
34E-10
1 2E 06
29E 10
1 6E 06
7 4E-09
Milk
Cone
mg/kgWW
32E 12
54E 11
36E 11
9 1E-12
1 3E-11
1 1E-10
1 9E-08
1 OE-11
4 7E-11
27E-10
1 4E-10
27E-10
62E-11
1 8E-10
1 4E-10
2 7E-11
1 6E-09
69E 10
45E-10
1 3E-08
54E-06
32E 06
4 5E-04
25E 10
4 1E-07
4 9E 04
35E-09
2 GE-08
47E09
29E-10
16E05
3 BE 07
55E-10
28E09
6 7E-08
46E-14
1 BE-10
1 BE 09
1 9E-08
62E 07
62E07
66E 09
29E-06
4 7E 07
1 3E 07
1 1E 08
Cheese
Cone
mg/kgWW
4 BE 11
8 1E-10
54E 10
1 4E-10
1 9E-10
1 6E-09
2 9E-07
1 5E-10
7 1E-10
40E-09
22E-09
4 1E-09
93E-10
27E-09
2 1E-09
40E-10
24E-08
1 OE-08
6BE-09
1 9E-07
54E-06
32E-O6
45E-04
25E-10
41E-07
49E-04
35E-09
26E-08
47E-09
29E-10
1 6E-O5
38E-07
55E-10
28E-09
6 7E-08
46E-14
1 BE-10
1 8E-09
1 9E-08
62E-07
62E-07
6 6E-09
29E 06
4 7E-07
1 3E 07
1 1E-08
Milk
Dessert
Cone
mg/kgWW
2 IE 11
35E 10
24E 10
5 9E-11
8 4E-11
69E 10
1 3E 07
65E-11
31E-10
1 8E-09
94E-10
1 8E-09
40E-10
1 2E-09
90E-10
1 8E-10
1 OE-08
45E-09
29E^)9
8 1E-08
54E-O6
32E-06
45E-04
25E-10
4 1E-07
4 9E-04
3 5E-09
26E-08
47E-09
29E-10
1 6E-05
3 8E-07
55E-10
2 BE -09
67E-08
46E-14
1 8E-10
1 8E 09
1 9E 08
62E 07
62E-07
66E 09
2 9E 06
4 7E 07
1 3E 07
1 1E 08
Yogurl
Cone
mg/kgWW
32E 12
54E-11
36E-11
9 1E-12
1 3E-11
1 1E-10
1 9E-08
1 OE 11
4 7E-11
27E-10
1 4E-10
27E-10
62E 11
1 8E 10
1 4E-10
2 7E-11
1 6E-09
69E-10
45E 10
1 3E 08
54E06
32E-06
4 5E-04
25E-10
4 1E-07
49E 04
35E-09
26E-08
4 7E-09
29E-10
1 6E-05
3 8E-07
55E 10
28E-09
6 7E-08
46E-14
18E-10
18E-09
1 9E 08
62E 07
62E 07
66E 09
29E 06
4 7E 07
1 3E 07
1 1E 08
Cream
Cone
mg/kgWW
40E 11
6 7E-10
45E-10
1 1E-10
1 6E-10
1 3E 09
2 4E-07
1 3E-10
59E-10
3 4E-09
18E09
34E-09
78E-10
22E 09
1 7E-09
34E-10
2 OE-08
87E-09
56E-09
1 6E-07
54E06
32E^)6
4 5E 04
25E-10
4 1E-07
4 9E 04
35E09
26E^)8
4 7E-O9
29E-10
1 6E-O5
3 BE-07
55E-10
2BE-09
6 7E-08
46E 14
1 8E-10
1 BE 09
1 9E-08
62E 07
6 2E 07
66E 09
29E 06
4 7E 07
1 3E 07
1 1F OB
Butler
Cone
mg/kgWW
1 3E-10
2 2E-09
1 5E-09
3 7E-10
53E-10
43E-09
7 9E-07
4 1E-10
19E-09
1 1E-08
59E-09
1 1E-08
25E-09
73E-09
57E09
1 1E-09
66E-08
2 BE -08
1 8E^)8
51E^)7
54E-06
32E-06
45E-04
25E-10
4 1E-07
4 9E 04
35E-09
2 6E-08
47E-09
29E-10
1 6E 05
38E07
55E-10
2 BE 09
6 7E 08
46E 14
18E 10
1 BE 09
1 9E 08
62E 07
62E 07
6 6E 09
29E 06
4 7E 07
1 IE 07
1 1F OB
Exposed
Produce
Cone
mg/kgWW
66E-14
1 1E-12
1 6E-12
49E-13
52E-13
26E-11
32E-09
95E-13
57E-12
76E-12
56E-12
12E 11
27E 12
90E-12
31E 11
26E-12
70E 10
1 7E-11
1 7E-11
4 7E-10
54E-08
26E-O8
28E-O5
4 4E-07
22E-09
54E 06
24E-11
26E09
1 1E 08
75E 11
1 3E 08
22E09
25E 09
1 4E 08
68E 08
89E 12
8 BE 09
25E 10
20E 08
1 1E 05
1 IE 05
76E 09
4 OE 07
22E 08
8 1E 09
1 IF 06
Protected
Produce
Cone
mg/kgWW
49E 15
20E-14
39E-15
1 2E 14
40E 15
2 7E 14
2 BE 13
55E-14
1 1E 13
1 OE 13
1 1E-13
1 1E 13
2 7E 14
1 2E 13
32E 13
40E-14
1 7E 13
1 6E 11
4 BE 12
24E 12
2 IE 10
10E 09
14E 11
7 BE 07
1 5E 10
2 IE 12
45E 13
45E09
20E 08
1 3E 10
1 4E 10
1 BE 10
2 BE 09
9 1E 09
59E08
23E 12
90E 09
1 5E 10
1 9E 08
1 9E 05
1 9E 05
1 1E 08
5 IE 07
33E 08
6 7E 10
2 ?F 06
Volume V  Appendix V-11
-------
 TAOIF  1   Average Modflrd FnvimnmrMilal F rposuir Co
Chemical
2.3.7.8TCDD
1 2.3.7.6-PeCDD
1,2.3,4. 7, 8-HxCDD
1. 2,3,6. 7,8-HxCDD
1,2,3,7,8,9-HxCDD
1,2, 3,4,6 ,7,8-HpCDO
OCDD
2,3,7,8-TCDF
1,2,3,7,8 PeCDF
2,3,4.7,8 PeCDF
1, 2,3,4, 7,8-HxCDF
1,2,3,6,7,8-HxCDF
1.2,3,7,8.9 HxCDF
2,3,4,6,7,8-HxCDF
1.2.3,4,6,78 HpCDF

1, 2,3,4, 7,8,9-HpCDF
OCDF
Tetrachtoroblphenyl
Hexachk>roblphenyl
Heptachtoroblphenyl
Benzo( a )pyrene
Ben2o(b)fkioranlhene
Bl8(2-e(hy(h«xyt)phlhalale
Carbon letrschlotide
Dibenz(*,h)anthracen«
D)(n)octyt ptithalate
Heplachlor
Hexachlorobenzene
Hexachtorobutadiene
Hexachtorocyclopenladiene
Hexachtorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
W2 avg
W2 avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2 avg

W2 avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
Lealy
Produce
Cone
mg/kgWW
34E 12
62E 11
86E-11
23E 11
26E-11
1 4E-09
1 BE-07
5 1E-11
31E-10
4 1E-10
28E-10
64E-10
1 5E-10
4 7E-10
1 5E-09

1 2E-10
3 8E-08
4 5E-10
8 1E-10
26E-08
29E-06
1 4E-06
1 6E 03
2 5E-07
32E-09
3 OE-04
1 3E-09
76E-09
73E-09
1 3E-10
1 8E-08
32E-09
72E-09
3 1E-08
2 4E-07
1 6E-11
1 6E-08
32E-10
4 4E-08
35E-05
35E-05
53E-09
32E-07
46E 08
1 2E 08
1 2E-06
Root
Produce
Cone
mg/kgWW
4 4E 15
18E-14
BSE 15
20E-14
1 2E-14
83E 14
54E-13
45E-14
1 1E-13
1 2E-13
18E-13
1 7E-13
4 3E-14
20E-13
8 OE-13

99E-14
8 7E-13
1 2E-10
1 9E-11
1 1E-10
2 4E 11
1 1E-09
2 1E-11
9 2E-08
26E-10
2 2E 08
1 1E-11
1 OE-07
32E-O8
15E-09
6 OE-08
28E-10
2 BE 12
2 7E 12
44E-11
1 6E-16
1 3E-11
8 1E-15
10E-11
30E-09
30E-09
23E-13
62E-11
33E 11
20E 14
27E-10
River
Fish
Cone
mg/kg
58E 12
2 7E 11
45E 11
55E-11
35E 11
8 1E-11
62E-12
4 4E-11
2 1E-10
3 1E-10
49E-10
46E-10
1 1E-10
52E-10
5 8E-10

74E-11
25E-11
39E 09
35E 07
1 4E 07
62E-07
28E 06
4 1E-07
64E 09
33E-05
7 3E 08
1 IE 08
65E-05
45E-06
52E-09
54E-07
4 2E-05
43E-11
4 1E-08
7 7E-09
22E-11
9 1E-08
39E-10
2 4E-07
8 IE-OS
46E 04
68E-09
1 OE 06
76E 11
1 4E-07
4 8E-07
Lako
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
1 NA
NA
NA
NA
NA
NA
NA
NA
KJA
rm
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Rivnf
Water
Cone
mg/l
34E 16
1 6E 15
4 2E 16
1 6E-15
1 1E-15
23E-15
37E 14
33E-15
88E-15
97E-15
1 5E-14
1 4E-14
1 9F 1">
J f. C • 1 3
1 6E-14
3 AC 1 J
•It - II
4 3E-15
93E-15
72E 13
5BE-13
69E-13
1 1E-11
4 3E-11
20E-11
2 1E-10
25E 11
1 2E-12
22E-14
1 2E-10
1 4E-10
20E-12
1 1E-10
27E-11
4 3E-11
93E-10
1 9E-09
1 1E-12
4 1E-11
24E-11
1 5E 09
2 2E-08
2 2E 08
1 1E-10
1 3E 08
1 5E-10
1 2E-09
1 1E-09
lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
MM
NA
MA
r!f\
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg'kgWW
8 5E 12
1 5E 10
9 9E-1 1
2 5E - 1 1
3 5E-11
29E-10
5 3E 08
2 7E-11
1 3E-10
7 3E-10
39E-10
7 4E-10
i 7C in
1 /t-lO
4 8E-10
37C 4n
7fc-10
73E-11
44E-O9
1 7E-09
1 1E-09
34E-08
22E-08
13E-08
16E-04
77E-11
18E-07
2 OE-04
14E-09
64E-09
9 5E-10
60E-11
7 IE-OS
1 6E-07
76E-10
1 2E-08
40E-09
59E-12
4 1E-10
71E-10
2 5E 09
6 4E 08
6 4E-08
5 1E-09
24E 07
95E 09
26E-07
5 3E 09
Volume V, Appendix VM1
                                                                                        22!
-------
  TABtE 1
            Average- M.m.-lrvl Fnvironmrntal F .pnMiip Cnnrrnlrahons
Chemical

2.3.7.8 TCDD
1,2,3.7.8-PeCDD
1,2.3.4.7.8 HxCDO
1,2.3,6.7 8 HxCDD
1,2.3,7,8.9 HxCDD
1,2,3,4,6,7,8 HpCDD
OCDD
2,3.7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4,7.8-PeCDF
1,2,3,4. 7, 8-HxCDF
1,2,3,6,7,8 HxCDF
1.2,3,7,8.9 HxCDF
2.3.4.6.7. 8-HxCDF
1,2.3.4,6,7,8-HpCDF
1,2,3,4, 7,8,9 HpCDF
OCDF
Telrachloroblphenyf
Hexachlorobiphenyl
Heptachloroblphenyf
Benzo(a)pyrene
Benzo(b)fluoranthene
Bi»(2-ethy1hexy1)phthalate
Carbon lelrachloride
Dlben2(a,h)anthracene
CM(n)octyl phthalate
Heplachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
lndeno(1,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavaleni)
Lead
Mercury
Mercury (melhyt BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea

W3avg
W3avg
W3 avg
W3 avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avp
W3 avg
W3avg
W3 avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3 avg
W3avg
W3 avg
W3avg
1 cm Soil
Cone
mg/kg

34E-11
1 4E 10
1 3E 10
1 3E-10
15E-09
72E-09
33E-10
93E-10
1 1E-09
2nc no
19E-09
A RP m
2 1E-09
1 2E-08
1 5E-09
2 2E-08
4 IE 08
6 BE -08
6 7E-08
7 5E-07
40E-06
2 5E-07
24E-06
12E-06
1 OE-07
20E-09
38E-06
1 OE-05
1 7E-07
33E-06
1 4E^)6
2 5E-07
95E-06
1 2E-05
2 5E-08
1 4E-07
66E-07
4 2E-05
1 9E-04
1 9E 04
9 7E-07
1 BE 04
88E-07
4 4E-05
63E-06
Beel
Cone
mg/kgWW

1 9E 11
3 3E 10
22E-10
5 Dt-1 1
79E 11
64E-10
1 2E 07
6 1E-11
29E-10
1 6E-09
t 76 09
Bt-10
1 1E-09
84E-10
1 6E 10
9 7E-09
42E09
2 7E 09
76E-08
6 2E 06
37E-06
52E 04
26E-10
49E 07
5 7E-04
4 1E-09
2 9E-08
53E-09
33E-10
19E-05
4 5E-07
22E-09
3 8E-08
1 2E-08
21E-11
1 2E-09
26E-09
93E 09
1 BE -07
1 8E-07
1 6E-08
77E 07
28E-08
1 OE-06
1 7E-08
Poik
Cone
mgfkgWW

4 7E-12
« 1E 11
39E-11
1 3E-11
1 6E-11
1 1E-10
2 OE 08
1 3E-11
55E-11
3 IE-ID
1 9E-10
3 1E-10
7 2E-11
22E-10
1 9E-10
4 1E-11
1 7E 09
3 3E-09
2 OE-09
1 4E-08
4 1E 07
2 9E-07
34E-05
1 OE-10
55E08
3 7E-05
29E-10
2 6E-08
60E09
37E-10
1 2E-06
5 7E-08
91E-10
1 3E-08
5 2E-08
1 8E-11
54E-11
35E-09
2 6E 08
59E-07
59E-07
70E 08
1 9E 05
62E-10
4 3E-06
4 4E 09
Chicken
Cotic
mg'kgWW

1 7E 13
66E 13
29E 13
4 2E 13
33E 13
6 IE 13
' 4 2E 12
35E t3
76E 13
3 7E-12
5 1E-12
4 1E 12
1 OE-12
4 2E 12
56E-12
1 7E 12
49E 12
2 8E-10
1 7E 10
1 7E-10
1 5E 11
99E 11
75E 13
46E 13
9 IE-It
1 BE 12
56E-14
48E 11
1 2E-11
67E-13
1 7E 09
94E 11
66E-12
49E 09
20E 11
67E-13
22E-10
39E 11
82E 07
1 IE 07
1 IE 07
1 IE 10
62E 07
74E 12
84E 07
3 BE -09
Fgg
Cone
mg kgWW

2 3E 13
9 1E 13
4 OE 13
5 7E 13
46E 13
84E-13
5 7E-12
48E-13
1 OE-12
5 1E-12
7 1E-12
57E 12
1 4E-12
5BE-12
7 7E-12
23E-12
68E-12
38E-10
23E-10
23E-10
1 9E 08
1 2E 07
94E-10
57E-10
1 1E-07
22E-09
70E-11
61E-08
1 4E-08
84E-10
22E-06
1 2E-07
7 7E-11
64E-09
1 6E-08
79E-13
52E-12
63E-11
82E 07
93E 09
93E-09
1 7E-10
62E-07
1 5E 10
84E 07
38E 09
Milk
Cone
mg'kgWW

1 5E 12
25E It
1 7E 11
4 2E 12
59E 12
46E 11
89E09
46E-12
22E-11
1 2E 10
66E 11
1 3E-10
28E 11
B2E 11
63E 11
1 2E-11
73E 10
32E 10
2 1E-10
57E 09
25E06
15E-06
21E-04
1 2E-10
1 9E 07
2 3E-04
16E09
1 2E-08
2 IE 09
1 3E-10
76E-06
1 8E-07
28E-10
1 4E 09
3 4E-08
23E-14
94E 11
9 OE-10
97E 09
28E07
28E 07
34E 09
1 5E 06
24E 07
65E 08
55E-09
Chpesf
Cone
mg/kgWW

2 2E 11
3 ?E 10
25E-10
63E 11
89E 11
73E 10
1 3E 07
69E 11
32E-10
1 9E-09
1 OE-09
1 9E-09
43E-10
1 2E^>9
95E-10
1 9E-10
1 1E-08
48E-09
3 1E-09
86E-08
25E-06
1 5E-06
21E-04
1 2E-10
1 9E-07
23E-04
16E^N
12E-08
2 1E-09
13E-10
76E-06
18E-07
28E-10
14E-09
34E-08
23E-14
94E-11
9 OE-10
9 7E 09
28E-07
2 BE 07
3 4E-09
1 5E 06
24E-07
65E 08
55E 09
Milk
Desspil
Cone
mg'kgWW

94E 12
1 6E 10
1 1E 10
2 7E 11
39E-11
3 1E-10
5 8E-08
30E-11
1 4E-10
8 OE-10
4 3E-10
8 1E-10
1 9E-10
53E-10
4 1E-10
80E-11
48E09
2 1E 09
1 3E-09
3 7E-08
2 5E-06
1 5E-06
2 1E 04
1 2E-10
1 9E-07
2 3E-04
1 6E-09
1 2E 08
2 1E-09
1 3E-10
7 6E-06
1 8E-07
28E-10
1 4E-09
3 4E-08
23E-14
94E-11
9 OE-10
9 7E 09
2 BE 07
2 BE 07
34E 09
1 5E 06
24E 07
65E 08
55E 09
Voguit
Cone
mg/kgWW

1 5E 12
25E-11
1 7E-11
4 2E 12
59E 12
48E 11
89E-09
46E-12
22E-11
1 2E-10
66E 11
1 3E-10
28E-11
82E-11
63E-11
1 2E-11
73E-10
32E-10
2 IE 10
57E09
25E06
15E-06
2 1E-04
1 2E-10
1 9E-07
2 3E 04
16E-09
1 2E 08
2 1E-09
1 3E-10
76E-08
1 8E-07
28E-10
14E09
34E-08
23E-14
94E 11
90E-10
9 7E09
2 BE 07
28E 07
34E 09
1 5E 06
24E 07
65E 08
55F 09
Cream
Cone

1 BE 11
3 1E 10
2 1E 10
52E-11
74E-11
6 OE-10
1 1E-07
58E-11
2 7E-10
1 5E-09
83E-10
1 6E-09
36E-10
IDE -09
79E-10
1 5E-10
92E09
4 OE-09
26E-09
7 2E-08
25E-06
15E-06
2 1E-04
1 2E-10
1 9E-07
23E-O4
1 6E-09
1 2E-08
21E09
1 3E-10
76E-06
1 BE 07
28E-10
1 4E-09
34E-08
23E-14
94E 11
9 OE-10
97E09
2 8E 07
2 BE 07
3 4E 09
1 5E 06
2 4E 07
6 5E 08
5"5F 09
Butler
Cone

60E-11
1 OE-09
6RF m
1 7E-10
24E 10
20E09
3 6E-07
1 9E-10
88E-10
5 1E-09
27E-09
5 1E-09
1 2E-09
34E-09
26E-09
5 1E-10
3 OE-08
1 3E 08
85E-09
2 4E-07
25E-06
1 5E-06
2 1E-04
1 2E 10
1 9E-07
2 3E-04
1 6E-09
12E-OB
21E-09
1 3E-10
76E-06
1 8E-07
28E-10
14E-09
3 4E-OB
23E 14
94E-11
90E 10
9 7E-09
2 BE 07
2 BE 07
34E 09
1 5E 06
2 4E 07
65E Ofl
55F 09
Exposed
Produce
Cone
mg/kgvWV
30E 14
52E-13
2 2E-13
24E 13
1 2E-11
1 5E-09
44E-13
2 BE 12
3 5E-12
26E-12
•i "iF-19
13E-12
41E-12
1 4E-11
1 2E-12
32E-10
8 OE-12
79E-12
22E-10
2 5E-08
1 2E^)8
1 3E 05
20E07
1 1E 09
25E06
1 1E-11
1 2E 09
52E-09
34E 11
59E09
1 IE 09
1 3E 09
69E 09
35E08
45E 12
45E 09
1 3E 10
1 OE 08
50E 06
50E 06
39F 09
?OE 07
1 1E 08
4 If 09
R riF 07
Pioteclod
Produce
Cone
mg/kgWW
2 3E 15
95E 15
59E 15
1 9E 15
1 3E 14
13E 13
25E 14
50E 14
4 DC \A
54E-14
5 IP 1J
13E-14
5BE-14
15E 13
1 9E 14
82E 14
74E-12
22E 1-:
1 IE 12
96E 11
46E 10
64E 12
36E07
72E 11
96E 13
2 IE 13
20E09
92E 09
59E 11
66E 11
86E 11
1 4E 09
47E09
30E 08
1 2E 12
46E09
79E 11
96E 09
86E 06
86E 06
59E 09
26E 07
1 7E 08
34E 10
1 1E 06
Volume V. Appendix V-11
-------
TABLE 1   Average Modeled Fnvifonrnrntal T*posuFp Concentrations
Chemical
2.3.7.8 TCDD
1.2,37,8-PeCOD
1.2.3,4,7.8 HxCDD
1,2,3.6,7.8 HxCOD
1,2,3,7.8,9 HxCDD
1,2.3.4,6,7,8-HpCDO
OCOO
2,3,7,8- TCDF
1,2,3.7,8-PeCDF
2,3.4, 7,8-PeCDF
1, 2,3,4, 7.8-HxCDF
1, 2,3,6, 7.8-HxCDF
1 2,3 7.8,9 HxCDF
2,3.4.6,7,8 HxCDF
1.2,3.4.6.7,8 HpCDF
1,2,3.4, 7, 8,9 HpCDF
OCDF
Tetrachloroblphenyt
Hexachtorobiphenyl
Heptachloroblphenyl
Benzo(a)pyrene
Benzo(b)(hioranthene
Bl8(2-ethythexyf)phthalate
Carbon letrachlorlde
Diben/(a,h)anlhracene
Dt(n)octy) phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachtorocyctopentadiene
Hexachtorophene
lndeno(1 ,2,3-c
-------
TABl E 2  Maximum Mortrlrd F nviionnipfil.il F • po'uiir
Chemical
2,3,7.8 TCDD
1.2.3,7.8 PeCDD
1.2,3.4,7.8 HxCDD
1,2.3,6,7,8 HxCDD
1.2,3.7,8,9 HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2.3.7,8-TCDF
1,2.3.7,8-PeCDF
2,3.4,7,8-PeCDF
1. 2,3,4, 7,8-HxCDF
1,2,3,6,7,8-HxCDF
1.2,3,7,8,9 HxCDF
2,3.4.6,7.8-HxCDF
1,2,3.4,6,7,8-HpCDF
1, 2,3,4, 7,8.9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachloroblphenyl
Heplachlorobiphenyt
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-ethy!hexy1)phthalate
Carbon telrachlorlde
Dlbenz(a,h)anthracene
Di(n)octy1 phlhalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopenladiene
Hexachloropnene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
El max
E 1 max
E1 max
E1 max
E1 max
E1 max
E1 max
E1 max
El max
El max
El max
E1 max
El max
E1 max
El max
Ef max
E1 max
El max
E1 max
E1 max
El max
E1 max
E1 max
El max
E1 max
E1 max
El max
E1 max
El max
El max
El max
E1 max
El max
El max
E1 max
E1 max
E1 max
E1 max
E1 max
E1 max
E1 max
El max
E1 max
E1 max
E1 max
El max
1 cm Soil
Cone
mg/kg
73E-10
3 1E-09
30E-09
50E-09
32E-09
3 6E-08
1 7E-07
69E-09
2 OE-08
23E-08
46E-08
43E-08
1 OE-08
49E-08
2 9E-07
36E-08
5 3E-07
86E-07
1 4E-06
1 4E-06
1 6E-05
84E-05
54E-06
49E-05
29E-05
2 1E-06
4 IE-OS
79E-05
2 1E-04
35E-06
79E-05
33E-05
49E-06
1 9E-04
23E-04
5 OE-07
28E-06
1 3E-05
8 3E-04
4 OE 03
4 OE-03
1 9E-05
36E-03
1 BE 05
8 8E-04
1 2E-04
Bcel
Cone
mg/kgWW
40E-10
6 BE 09
46E 09
1 2E 09
1 6E 09
1 3E 08
24E-06
1 3E-09
59E-09
3 4E-08
1 BE -08
34E-08
7BE-09
23E 08
1 BE -08
35E-09
2 OE-07
87E 08
5 6E-08
1 6E-06
1 3E-04
77E-05
1 IE 02
55E09
1 2E 05
1 2E 02
8 4E-08
61E07
1 1E-07
68E-09
4 7E-04
1 1E-05
4 5E-08
79E-07
24E-07
42E-10
25E-08
5 3E-08
1 9E-07
3 7E-06
37E 06
33E 07
1 6E-05
5 BE 07
2 1E-05
34E-07
Poik
Cone
mg/kgWW
99E 11
•1 3E 09
82E-10
2 7E-10
34E-10
2 3E-09
4 1E-07
28E-10
1 1E-09
64E-09
4 1E-09
66E-09
1 5E-09
46E09
40E-09
90E-10
35E-08
6 BE -08
42E-08
3 OE-07
84E-06
60EO6
7 OE-04
22E 09
1 3E-06
7 7E-04
60E-09
55E-07
1 2E-07
76E-09
2 8E 05
1 4E-06
1 8E 08
2 6E-07
1 OE-06
35E-10
1 1E 09
6 9E 08
52E-07
1 2E 05
1 2E 05
1 4E 06
3 8E 04
1 2E 08
8 5E 05
8 7E 08
Chicken
Cone
mg/kgWW
35E 12
1 5E 11
66E 12
97E 12
78E 12
, 1 4E-11
99E-11
73E-12
16E 11
80E 11
1 2E 10
95E-11
2 3E 11
96E 11
1 3E 10
39E It
1 2E 10
5 BE 09
34E 09
35E 09
33E 10
2 1E 09
1 7E-11
95E 12
22E 09
36E-11
1 2E 12
1 OE 09
24E 10
1 4E 11
4 2E 08
22E-09
1 3E-10
9 BE 08
39E-10
1 3E 11
44E 09
7 7E-10
16E05
2 3E 06
2 3E 06
2 1E 09
1 2E 05
1 5E 10
1 7E-05
7 6E 08
Egg
Cone
mg/kgWW
48E 12
20E 11
92E 12
1 3E 11
1 1E-11
20E-11
1 4E-10
1 OE-11
22E-11
1 1E-10
1 6E-10
1 3E-10
32E-11
1 3E 10
1 8E-10
54E-11
1 6E-10
80E-09
4 7E-09
48E-09
4 1E-07
26E-06
2 1E-08
1 2E-08
2 7E-06
4 5E-08
1 4E 09
1 3E-06
30E 07
1 7E-08
5 2E 05
28E 06
1 5E 09
1 3E-07
3 1E-07
1 6E-11
10E-10
1 3E-09
1 6E 05
1 9E 07
1 9E 07
34E 09
1 2E 05
29E 09
1 7E 05
7 6E-08
Milk
Cone
mg/kgWW
30E 11
5 IE 10
3 4E 10
8 BE-11
1 2E-10
1 OE-09
1 8E-07
95E-11
45E-10
26E 09
1 4E 09
26E-09
59E-10
1 7E-09
1 3E-09
26E-10
1 5E-08
66E-09
43E-09
1 2E-07
51E-05
30E 05
4 2E 03
24E 09
4 7E-06
4 7E-03
33E-OB
2 4E-07
4 4E 08
27E-09
1 9E-04
43E 06
5 7E-09
30E 08
7 OE-07
48E 13
19E 09
1 8E 08
20E 07
59E 06
59E 06
69E 08
30E 05
48E 06
1 3E 06
1 1E-07
Cheese
Cone
mg/kgWW
45E 10
7 7E 09
52E 09
1 3E 09
1 9E 09
1 5E 08
27E06
1 4E 09
6 7E-09
3 BE -08
2 1E-08
3 9E-08
89E-09
2 6E 08
2 OE-08
39E-09
2 3E-07
99E-08
6 4E-08
1 8E-06
51E-05
30E-05
42E-03
24E4»
47E-06
47E-03
33E-08
2 4E 07
44E-08
27E-09
1 9E-04
43E-06
57E-09
3 OE-08
7 OE-07
48E-13
19E-09
1 BE 08
20E 07
59E-06
5 9E-06
69E 08
3 OE 05
48E 06
1 3E 06
1 1E-07
Milk
Dessert
Cone
mg/kgWW
2 OE 10
3 3E 09
2 2E-09
5 7E-10
BOE-10
6 5E 09
1 2E 06
62E-10
29E-09
1 7E-08
9 OE-09
1 7E-08
3 8E-09
1 1E 08
86E-09
1 7E-09
9 9E-08
4 3E-08
2 BE 08
7 7E 07
5 1E-05
3 OE-05
4 2E-03
2 4E-09
4 7E-06
4 7E-03
3 3E-08
24E-07
4 4E-08
2 7E-09
1 9E-04
43E-06
57E-09
3 OE-08
7 OE-07
48E-13
1 9E-09
1 BE 08
20E 07
59E 06
59E 06
69E 08
30E 05
4 8E 06
1 3E 06
1 IE 07
Yog lift
Cone
mg/kgWW
30E 11
5 1E 10
34E 10
8 BE 11
1 2E 10
1 OE 09
1 8E-07
95E 11
45E-10
26E 09
1 4E-09
26E-09
59E 10
1 7E-09
1 3E-09
26E-10
1 5E-08
6 6E 09
4 3E 09
1 2E-07
5 1E-05
3 OE-05
4 2E-03
24E-09
4 7E-06
4 7E-03
33E 08
2 4E-07
4 4E-08
27E09
1 9E 04
43E 06
5 7E-09
30E 08
7 OE 07
48E-13
1 9E 09
1 BE 08
20E 07
59E 06
59E 06
69E 08
30E 05
48E 06
1 3E 06
1 1E 07
Cieam
Cone
mg/kgWW
3 BE 10
64E 09
4 3E 09
1 1E-09
1 5E 09
1 3E 08
2 3E 06
1 2E 09
5 6E 09
3 2E 08
1 7E 08
3 2E-08
7 4E-09
2 1E 08
1 7E 08
3 3E-09
1 9E 07
8 2E 08
5 3E 08
1 5E 06
5 1E 05
3 OE-05
4 2E 03
2 4E-09
4 7E-06
4 7E-03
3 3E-08
2 4E-07
4 4E 08
2 7E 09
1 9E 04
4 3E-06
5 7E 09
3 OE 08
7 OE-07
4 BE 13
1 9E-09
1 8E 08
20E07
59E 06
59E 06
69E 08
30E 05
4 8E 06
1 3E 06
1 1F 07
Butter
Cone
mg/kgWW
1 2E 09
2 1E-08
1 4E-08
36E-09
5 1E-09
4 1E-08
75E-06
39E-09
1 BE -08
1 1E-07
57E458
1 1E-07
2 4E 08
7 OE 08
54E 08
1 IE 08
6 2E 07
2 7E-07
1 8E-07
49E-06
51E-05
3 OE-05
42E4)3
24E^9
47E-06
4 7E-03
3 3E-08
2 4E-07
4 4E 08
27E-09
1 9E-04
43E06
57E 09
3 OE 08
70E 07
48E-13
1 9E 09
1 BE 08
20E 07
59E 06
59E 06
69E 08
30E 05
4 BE 06
1 IE 06
1 1F 07
E»posed
Produce
Cone
mg/kgWW
63E 13
1 1E-11
1 5E-11
47E-12
50E-12
24E-10
3 IE -08
90E-12
54E 11
73E-11
54E 11
1 2E 10
26E 11
86E 11
30E 10
25E 11
66E 09
1 7E-10
1 6E 10
45E 09
5 1E 07
24E 07
2 7E 04
42E06
26E 08
52E 05
23E 10
2 5E 08
1 1E-07
7 1E 10
1 4E 07
26E 08
26E 08
1 4E 07
70E 07
93E 11
9 1E 08
26E 09
2 1E 07
1 OF 04
1 OF 04
7 BE 08
4 1E 06
2 3E 07
8 5F 08
1 IF 05
Protected
Produce
Cone
mg/kgWW
4 BE 14
2 1E 13
42E 14
14E 13
45E 14
30E-13
32E 12
53E 13t
1 IE 12
1 1E-12
12E 12
1 2E 12
2 BE 13
1 3E 12
35E 12
44E 13
19E 12
1 5E 10
46E 11
23E 11
2 1E 09
9 BE 09
1 4E 10
74E06
1 7E 09
20E 11
3E 12
2E 08
9E 07
2E 09
6E 09
20E 09
2 BE 08
9 3E 08
6 IE 07
24E 11
92E 08
1 6E 09
1 9E 07
1 BE 04
1 BE 04
1 2E 07
53E 06
34E 07
69E 09
22E 05
       . \l AnnonMiy V.1 1
-------
TABLE ?  Maximum Modrlrrl F nvptnninrnlal Fipo-uirr rnncrnfialions
Chemical
2.3.7,8 TCDD
1,2,3,7,8-PeCDD
1.2.3,4,7,8-HxCDD
1.2.3.6,7.8 HxCDD
1,2,3.7,8.9-HxCDD
1,2,3.4,6.7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3.7,8-PeCDF
2,3,4, 7,8-PeCDF
1,2,3,4,7,8-HxCDF
1,2.3,6.7,8-HxCDF
1,2,3.7,8,9-HxCDF
2.3,4.6,7,8-HxCDF
1,2,3 4.6,7.6 HpCDF
1,2,3,4,7,8,9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachtoroblphenyl
Heptachloroblphenyl
Benzo(a)pyrcne
Benzo(b)tluoranthene
Bls(2-«thythexy1)phthalafe
Carbon lelrachlortde
Dlbenz(a,h)anthracene
Di(n)ocfy1 phlhalate
Heplachlor
Hexachtorobenzene
Hexachlorobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
tndeno(1 ,2,3-cd)pytene
Anlimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalenl)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
El max
E1 max
El max
E1 max
El max
E1 max
Et max
E1 max
E1 max
E1 max
E1 max
El max
E1 max
E1 max
El max
El max
E1 max
Et max
E1 max
El max
E1 max
El max
El max
E1 max
E1 max
E1 max
Et max
Et max
E1 max
E1 max
E1 max
E1 max
E1 max
El max
E1 max
El max
E1 max
E1 max
E1 max
Et max
E1 max
E1 max
E1 max
E1 max
E1 max
E1 max
Leafy
Produce
Cone
mg/kgWW
32E-11
59E-10
8 1E-10
22E-10
25E-10
1 3E-08
1 7E-06
48E-10
29E-09
39E-09
27E-09
6 1E-09
1 4E-09
44EO9
1 4E-08
1 1E-09
3 6E-07
4 3E-O9
7 7E-09
2 5E-07
27E-05
1 3E-Q5
1 5E-02
23E-06
36E-08
29E-03
1 3E-08
72E-08
69E-08
12E-09
2 1E-07
37E-06
7 4E-08
3 2E-07
24E-06
1 7E-10
1 6E-07
33E-09
45E-07
3 3E-04
3 3E-04
5 4E 08
33E 06
48E-07
1 2E-07
1 2E-05
Root
Produce
Cone
mg/kgWW
43E-14
18E-13
95E-14
22E-13
1 4E-13
92E-13
60E-12
43E-13
1 1E-12
1 2E-12
20E-12
1 9E-12
46E-13
2 1E-12
87E-12
1 1E-12
98E-12
1 1E-O9
1 BE-10
1 1E-09
24E-10
1 1E-08
2 1E-10
87E-07
29E-09
21E-07
10E-10
99E-07
30E-07
1 4E-08
68E-07
32E-09
2BE-11
28E-11
45E-10
17E-15
1 4E-10
83E-14
1 1E-10
28E-08
28E-08
23E-12
63E-10
34E-10
21E-13
2 BE -09
River
Fish
Cone
mg/Vg
98E 12
42E 11
6 2E-11
74E 11
4 7E-11
1 1E-10
80E-12
76E-11
34E-10
49E-10
68E-10
63E-10
1 5E-10
72E-10
76E-10
98E-11
33E 11
70E 09
63E 07
24E-07
92E-07
50E06
5 3E-07
1 2E-08
43E 05
1 3E-07
2 OE-08
1 2E-04
8 1E-06
93E-09
7 OE-07
5 4E-05
51E-11
4 9E-08
92E-09
26E-11
1 1E-07
46E-10
2 8E-07
1 5E-04
8 3E-04
82E 09
1 3E 06
9 IE-It
1 7E 07
5 7E-07
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
5 7E-16
25E-15
5 BE-16
22E-15
1 4E-15
3 1E-15
48E-14
58E-15
1 4E-14
1 5E-14
20E-14
19E-14
46E-15
2 1E-14
45E-14
57E-15
1 2E-14
1 3E-12
1 1E-12
1 2E-12
1 6E-11
78E-11
26E-11
38E-10
32E-11
21E-12
40E-14
22E-10
25E-10
36E-12
1 4E-10
35E-11
5 1E-11
1 1E-09
23E-09
1 3E-12
49E 11
29E-11
1 8E 09
39E 08
3 9E-08
1 3E 10
1 6E-08
1 8E-10
1 4E-09
1 3E-09
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
8 1E-11
1 4E-09
9 4E-10
2 4E-10
34E-10
2 7E-09
5 OE-07
26E-10
1 2E-09
70E-09
3BE-09
71E-09
1 6E-09
46E-09
36E-09
7 1E-10
4 IE-OS
16E-08
1 OE-08
32E-07
21E-05
1 2E-05
1 7E-03
7 3E-10
20E-06
1 9E-03
1 3E-08
6 OE-08
90E-09
5 7E-10
82E-05
18E-06
79E-09
13E-07
4 2E-08
6 1E-11
43E-09
75E-09
2 7E 08
60E 07
60E 07
5 3E 08
25E-06
9 9E 08
27E06
5 5E-08
Volume V, Appendr
-------
  TABIE 2  Maximum Mndrlrd r nvimMmmlnl
                                          .poiutp
         Chemical
                           Subarea

2,3,7.8-TCDD
1.2.3,7,8-PcCDD
1.2 3,4 7,8-HxCDD
1,2,3,6,7,0-HxCDD
1,2.3,7,8,9 HxCDD
1. 2,3,4.6, 7,8-HpCDD
OCDD
2.3.7,8-TCDF
1,2,3.7,8 PeCDF
2,3,4, 7.8-PeCDF
1,2,3,4.7,8-HxCDF
1,2,3.6.7,8-HxCDF
1,2,3,7.89-HxCDF
2,3.4.6,7.8-HxCOF
1,2.3.4,6, 7,8- HpCDF
1,2,3,4, 7, 8.9-HpCDF
OCDF
Tetrachlorobiphenyl
Hexachlorobiphenyt
HeptacMoroblphenyt
Benzo(«)pyrene
Benzo(b)fluoranthene
Bl8(2-ethythexyt)phthalate
Carbon tetrachforfde
Dibenz(a.n)anlhracene
Dl(n)octyt phlhalate
Heptachlor
Hexachloroberuene
Hexachlorobutadiene
Hexachlorocyclopentadlene
Hexachtorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc

E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
mg/kg
24E-10
98E-10
87C -In
' K. IU
1 4E-09
89E-10
1 OE-08
23E-09
65E-O9
73E09
1 3E-08
1 2E-08
•> 1CJW
J 1 C^/3
1 4E-08
8 2E-08
1 OE 08
1 5E 07
29E 07
48E-07
4 7E-07
52E 06
1 7E-06
1 7E-05
79E-06
7 1E-07
1 4E-08
27E-05
73E-05
1 2E-06
22E-05
90E-06
1 4E-06
56E-05
69E-05
1 5E-07
8 2E-07
39E-06
2 5E-04
1 4E-03
1 4E-03
57E-06
1 1E-03
52E-06
2 6E 04
37E-05
i_uriL
14E-10
2 3E-09
39E-10
55E-10
45E-09
B 3E-07
43E-10
2 OE-09
1 2E 08
62E-09
1 2E-08
27P no
/ c-uy
7 RP no
I \3fi-\jy
e QC no
*j UC ~\j-y
12E09
69E-08
30E 08
1 9E-08
54E-07
44E-05
26E-05
37E-03
1 9E^>9
33E-06
4 OE-03
29E-08
2 1E-07
3 7E-08
23E-09
1 3E-04
31E-06
1 4E-08
2 4E-07
7 2E-08
1 3E-10
73E-09
1 6E-08
56E-08
1 3E-06
1 3E-06
9 7E-08
4 7E-06
1 7E 07
62E 06
1 OE-07
mgrtg/kgWW
1 OE 11
1 7E 10
1 2E-10
29E 11
42E 11
34E-10
6 2E 08
32E-11
15E-10
87E 10
47E 10
88E-10
2 OE-10
5 8E-10
4 5E-10
8 7E-11
52E 09
22E 09
1 5E-09
4 OE 08
1 7E-05
1 OE-05
1 4E-03
8 1E-10
1 3E-O6
1 6E-03
1 1E-08
8 3E-08
15E-08
93E-10
52E-05
1 2E-O6
1 7E-09
89E-09
2 1E-07
14E-13
58E 10
5 4E-09
59E 08
20E 06
20E-06
2 1E-08
89E-06
1 4E-06
3 9E 07
33E-08
Cone
mg/KgWW
1 5E-10
26E-09
1 8E-09
44E-10
63E-10
5 IE 09
94E-07
49E-10
2 3E-09
1 3E-08
7 OE-09
1 3E-08
3 OE-09
86E-09
6 7E-09
1 3E-09
7 8E-08
34E-08
2 2E-08
6 1E-07
1 7E-05
1 OE-05
1 4E-03
81E-10
1 3E-06
16E-03
1 IE-OS
83E-08
15E-08
9 3E-10
52E-05
12E-06
1 7E-09
89E-09
2 1E-07
14E-13
58E-10
54E-09
5 9E-OB
20E-06
20E 06
2 1E-08
89E 06
1 4E 06
39E 07
3 3E-08
mg<'kgWV\
6 7E-11
1 1E 09
76E 10
1 9E-10
2 7E-10
2 2E-09
4 1E-07
2 1E-10
99E 10
57E09
3 OE-09
57E-09
1 3E-09
37E 09
29E-09
5 6E 10
3 4E-08
1 5E-08
95E-09
2 6E-07
1 7E-05
1 OE-05
1 4E-03
81E-10
1 3E-06
1 6E-03
1 1E-08
8 3E-08
1 5E-08
93E-10
52E-05
12E-06
1 7E-09
89E-09
2 1E-07
14E-13
58E 10
54E 09
59E-08
20E 06
20E 06
2 1E 08
8 9E 06
1 4E 06
39E 07
3 3E-08
, mgW
1 OE 11
1 7E-10
1 2E-10
29E-11
42E 11
34E-10
62E 08
32E-11
1 5E-10
87E-10
47E-10
88E-10
2 OE-10
5 BE-10
45E-10
8 7E-11
52E-09
22E09
1 5E-09
40E08
1 7E-05
1 OE-05
1 4E 03
81E-10
1 3E-08
1 6E-03
1 1E-08
83E08
1 5E 08
93E-10
52E-05
12E-08
1 7E-09
89E-09
21E-07
1 4E-13
58E-10
54E 09
59E 08
20E 06
20E 06
2 IE 08
89E 06
1 4E 06
39E 07
33E OB
Cone
mg/kgvW\
1 3E 10
2 2E 09
1 5E 09
3 7E-10
52E 10
4 3E-09
7 BE 07
4 1E-10
1 9E 09
1 1E-08
58E-09
1 1E-08
2 5E-09
7 2E 09
56E-09
1 1E-09
6 5E-08
2 8E-08
1 8E-08
5 1E-07
7E-05
OE-05
4E-03
8 1E-10
3E 06
6E-03
1E-08
83E-08
1 5E-08
93E-10
5 2E-05
1 2E-06
1 7E-O9
89E-09
2 1E-07
1 4E-13
58E-10
54E 09
5 9E 08
20E 06
2 OE 06
2 IE 08
89E 06
1 4E 06
3 9E 07
3 IF OB
1 mg/kgWV\
42E-10
7 1E-09
48E-09
1 2E-09
1 7E-09
1 4E-08
26E-06
1 3E-09
62E-09
36E-08
1 9E-08
3 6E-08
82E-09
2 4E-08
1 8E-08
36E-09
2 1E437
92E-08
6 OE-08
1 7E-06
1 7E 05
1 OE-05
14E-03
81E-10
1 3E-06
1 6E-03
1 IE-OS
B 3E-08
1 5E-08
93E-10
52E 05
12E-06
1 7E 09
89E09
2 1E 07
1 4E 13
58E 10
54E 09
59E 08
20E 06
2 OE 06
2 IE 08
89E 06
1 4E 06
39E 07
1 3F OB
Cone
2 1E 13
37E 12
51E-12
16E-12
1 7E-12
83E-11
1 OE-08
3 1E-12
1 8E-11
25E-11
1 BE-11
39E-11
89E-12
29E-11
99E-11
83E-12
23E09
56E-11
56E-11
15E09
1 7E-07
8 3E 08
92E05
1 4E 06
72E-09
1 BE 05
79E-11
85E 09
3 7E 08
24E-10
4 1E-08
73E09
77E 09
4 2E 08
2 1E-07
2 BE 11
2 7E 08
7 7E 10
6 3E 08
35E 05
3 5E 05
2 3E 08
1 ?E 06
6 7E 08
2 6E 08
1 BF 06
mg'/kTJvvV
16E 14
65E 14
1 2E 14
39E 14
1 3E 14
83E 14
87E-13
18E 13
35E 1*
33E-13
36E 13
34E-13
84E-14
38E 13
10E 12
1 2E-13
54E 13
52E 11
1 6E 11
77E 12
66E 10
33E 09
43E 11
25E 06
47E 10
6 BE 12
15E 12
1 4E 08
65E08
42E 10
43E 10
56E-10
83E 09
2 7E 08
1 8E-07
7 1E-12
2 7E 08
4 6E-10
5 6E 08
6 1E 05
6 IE 05
3 4E 08
1 6E 06
99E 08
2 OE 09
6 RE 06
Volume V, Appendix V-11
-------
 TABLE 2  Maximum Modpird Fnvironrnprilal Exposure Cnnrrrilralions
Chemical
2.3.7,8-TCDD
1.2,3,7.6-PeCDO
1.2,3.4,7.8 HxCDD
1.2.3,6.7,8 HxCDD
1,2.3,7.8.9-HxCDD
1,2.3,4,6,7,8-HpCDD
OCDD
2,3,7.8-TCDF
1.2,3,7.8-PeCDF
2,3,4,7,8-PeCDF
1,2,3,4,7,8-HxCDF
1.2,3,6,7,8-HxCDF
1.2.3.7,8,9-HxCDF
2,3,4.6,7.8-HxCDF
1.2,3.4.6,7,8 HpCDF
1,2,3,4.7,8,9-HpCDF
OCDF
Telrachtoroblphenyl
Hexachloroblphenyt
Heptachloroblphenyl
Benzo(a)pyrene
Benzo(b)fluoranlhene
BlB(2-ethy1hexy1)phthalate
Cartoon tetrachloride
Dibenz(a,h)anlhracene
Di(n)octy1 phthalate
Heptachlor
Hexachtorobenzene
Hexachlorobutadlene
Hexaehtorocyclopentadiene
Hexachforophene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium '
Zinc
Subarea
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
Leafy
Produce
Cone
mg/kgWW
1 1E-11
20E-10
28E-10
75E-11
86E-11
45E-09
58E-07
1 6E-10
99E-10
1 3E-09
91E-10
21E-09
47E-10
1 5E-09
49E-09
38E-10
1 2E 07
1 4E-09
26E 09
84E-08
93E 06
45E-06
5 1E-03
7 9E-07
10E-08
9 8E-04
4 3E-09
2 4E-08
2 4E-08
4 1E-10
59E-08
10E-08
22E-08
96E-08
72E-07
49E-11
4 8E-08
99E-10
1 3E-07
1 1E-04
1 1E-04
1 6E 08
9 BE -07
1 4E-07
36E-08
36E-06
Root
Produce
Cone
mgfkgWW
1 4E-14
58E-14
2 7E-14
62E-14
39E-14
26E-13
1 7E-12
14E-13
35E-13
37E-13
58E-13
54E-13
1 3E-13
6 2E-13
25E-12
31E-13
27E-12
38E-10
6 1E-11
36E-10
78E-11
37E^)9
66E-11
30E-07
80E-10
70E-08
36E-11
3 4E-07
1 OE-07
49E-09
1 9E-07
87E-10
83E-12
82E-12
1 3E-10
49E-16
40E-11
25E-14
31E-11
96E-09
96E-09
69E-13
1 9E-10
99E 11
61E-14
82E-10
River
Fish
Cone
mg/kg
29E-12
1 2E 11
1 7E 11
2 1E-11
1 3E-11
29E-11
22E-12
23E-11
1 OE-10
1 4E-10
1 9E-10
1 8E-10
43E 11
2 OE-10
2 2E-10
2 7E-11
90E-12
2 1E09
1 9E-07
7 5E-08
29E07
1 5E-06
1 9E 07
35E-09
1 3E 05
40E-08
6 1E-09
36E-05
25E-06
29E-09
2 2E-07
1 6E-05
1 5E-11
1 4E-08
2 7E-09
75E-12
3 5E-08
1 3E-10
8 1E 08
45E-05
2 6E-04
24E 09
36E 07
27E-11
50E-08
1 7E 07
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
1 7E 16
7 2E 16
1 6E 16
6 1E-16
38E-15
85E-16
1 3E-14
1 7E-15
4 3E-15
44E-15
56E-15
53E-15
1 3E-15
A nc 1C
Q UC 1 3
1 3E-14
1 6E-15
33E-15
39E-13
32E-13
38E-13
50E-12
24E-11
92E-12
1 2E-10
93E-12
63E-13
1 2E-14
66E-11
78E-11
1 1E-12
43E-11
1 OE-11
15E-11
32E-10
6 7E-10
3 7E-13
1 6E-11
83E 12
50E-10
1 2E-08
1 2E 08
39E-11
46E 09
54E-11
4 1E-10
39E-10
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
MM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
2 8E-11
4 7E-10
3 2E-10
8 OE-11
1 1E-10
93E-10
1 7E-07
88E-11
4 1E-10
24E-09
1 3E-09
24E-09
55E-10
i RP no
i oc-uy
12E-09
2 4E-10
14E-08
54E-09
36E-09
1 1E-07
70E-06
41E-06
5 9E-04
25E 10
57E-07
64E-04
45E-09
21E-08
31E-09
1 9E-10
23E-05
52E-07
24E-09
3 9E-08
1 2E-08
18E-11
1 3E-09
22E-09
79E-09
2 1E-07
2 1E-07
1 6E-08
74E-07
3 OE-08
82E 07
1 r,f 08
Volume V. Appendi/   \
-------
                  \  -
TABLE 2  Maximum Moilrlrd Fnviinnuifril.il F.pnsurp rnnrrnfintion
Chemical
2.3.7,8 TCDD
1.2,3,7,8 PeCDD
1.2.3,4,7,8 HxCDD
1.2,3,6.7,8-HxCDD
1,2,3.7,8.9 HxCDD
1, 2,3,4.6, 7,8-HpC DO
OCDD
2,3,7,8-TCDF
1.2,3.7,8 PeCDF
2,3,4. 7,8-PeCOF
1, 2,3,4, 7,8-HxC OF
1,2,3.6,7.B-HxCDF
1,2.3.7,8,9-HxCDF
2,3,4.6,7,8-HxCDF
1.2.3,4,6,7,8 HpCDF
1,2,3.4,7,8,9 HpCDF
OCDF
Tetrachlorobiphenyl
Hexachlorobiphenyt
Heptachlorobtphenyt
Benzo(a)pyrene
Benzo(b)riuoranthene
Bi«(2 -ethy1hexy1)phthalate
Carbon tetrachloride
Dibenz(a,n)anthracene
Dl(n)octyt phlhalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Volume V, Appendix V-1 1
Subafea
E3 max
E3max
E3 max
E3 max
£3 max
E3 max
E3max
E3 max
E3 max
E3 max
E3max
E3max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3max
E3 max
E3max
E3max
E3 max
E3 max
E3 max
E3max
E3max
E3 max
E3max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
1 cm Soil
Coric
mg/kg
72E 11
30E-10
7 7F m
45E-10
2RP m
32E-09
15E-08
69E-10
19E-09
22E-09
4 1E-09
39E-09
95E-10
44E-09
2 6E-08
32E^)9
46E^8
86E 08
1 4E-07
1 4E-07
1 6E-06
85E 06
5 1E-07
49E-06
25E-06
2 1E-07
42E-09
79E-06
22E-05
36E-07
88E-06
28E-06
4 9E-07
19E-05
23E-05
50E-08
28E-07
1 3E-06
B 3E 05
4 1E-04
4 1E-04
1 9E 06
36E04
1 8E-06
8 BE 05
1 2E-05
Beef
Cone
mg/kgWW
40E-11
6 BE 10
12E-10
1 3E-09
25E-07
13E-10
60E-10
34E^)9
1 8E-09
35E-09
79E-10
23E09
34E-10
20E-08
8 BE 09
57E-09
1 6E-07
1 3E-05
77E-06
1 1E-03
55E-10
1 OE-06
12E-03
85E-09
61E-08
1 1E-08
68E-10
4 IE-OS
96E-07
45E-09
79E-08
2 4E 08
42E-11
25E-09
53E-09
1 9E-08
3 7E-07
3 7E-07
3 3E-08
1 6E-06
5 8E-08
2 IE 06
34E-08
Poik
Cone
mg'kgWW
99E 12
1 3E 10
8 2E 1 1
26E-11
3 3E-1 1
24E-10
4 IE 08
28E-11
1 1E-10
64E-10
40E-10
65E-10
1 5E-10
45E-10
86E-11
3 5E-09
6 BE 09
42E^)9
30E-08
65E07
6 IE 07
7 IE-OS
22E-10
1 1E-07
7 8E-05
6 1E-10
5 5E-08
1 3E-08
76E-10
24E 06
12E-07
1 8E-09
26E 08
1 OE-07
35E-11
1 1E-10
69E-09
5 2E-08
1 2E-06
1 2E 06
1 4E-07
3 8E 05
1 2E 09
85E 06
8 7E 09
Chicken
Cone
mg/kgWW
35E 13
1 4E 12
60E 13
86E 13
69E 13
1 3E 12
85E 12
72E 13
1 6E 12
76E-12
1 1E-11
BSE 12
2 1E 12
86E 12
1 2E-1 1
35E 12
1 OE 11
5 BE 10
35E 10
35E 10
3 1E-11
2 IE 10
1 6E 12
96E 13
1 9E 10
37E 12
1 2E 13
10E 10
24E 11
1 4E 12
36E-09
1 9E-10
1 3E 11
9 BE 09
39E 11
1 3E-12
44E 10
7 7E-11
1 6E-06
2 3E 07
23E-07
2 1E 10
1 2E-06
1 5E-11
1 7E 06
76E 09
Fqg
Cone
mg'kgWW i
4 8E 13
1 9E 12
8 ?E 13
1 2E 12
9 4E 13
1 7E 12
1 2E-11
1 OE-12
22E-12
1 1E-11
1 5E-11
1 2E-11
29E-12
1 2E-11
1 6E-11
48E-12
14E-11
BOE-10
48E-10
49E-10
39E-08
26E-07
20E-09
1 2E-09
2 3E-07
46E-09
1 5E-10
1 3E-07
30E-O8
1 7E-09
45E-06
24E-07
1 5E-10
1 3E-08
3 1E-08
16E-12
10E-11
1 3E-10
1 6E 06
1 9E 08
1 9E 08
34E 10
1 2E-06
29E 10
1 7E 06
76E 09
I
Milk
Cotic
•ng'kgVVW
30E 12
52E 11
3 5E 11
8 BE 12
1 2E-11
10E 10
1 9E 08
96E-12
45E 11
26E 10
1 4E 10
26E 10
60E-11
1 7E 10
1 3E-10
26E-11
1 5E-09
66E-10
43E-10
1 2E-08
51E06
30E 06
4 3E 04
24E-10
4 1E-07
4 7E-04
3 3E-09
2 5E-08
45E-09
28E-10
1 6E-05
3 8E-07
57E-10
30E-09
7 OE-08
48E-14
1 9E-10
1 6E-09
20E 08
59E-07
59E 07
69E 09
30E 06
4 BE 07
1 3E 07
1 IE 08
7
Cheese
Cone
mg'kgWW
4 6E 11
7 7E 10
52E 10
1 3E-10
1 9E-10
1 5E 09
2 BE 07
14E-10
68E-10
39E 09
2 1E-09
39E^)9
8 9E-10
26E-09
20E-09
39E-10
23E-08
1 OE-08
65E-09
1 8E-07
51E-06
3 OE-06
43E4M
24E-10
41E-07
47E-04
33E-09
2 5E-08
45E-09
2 8E-10
1 6E-05
3 8E-07
57E-10
30E-09
7 OE-08
48E-14
1 9E-10
1 BE -09
2 OE 08
59E-07
59E-07
69E 09
30E 06
4 BE 07
1 3E 07
1 IE 08
Milk
Dessert
Cone
mg'kgWW
20E 11
3 4E 10
2 3E 10
5 7E 11
8 1E-11
66E-10
1 2E-07
63E-11
29E-10
1 7E-09
90E-10
1 7E-O9
39E-10
1 1E-09
86E-10
1 7E-10
1 OE-08
4 3E-09
28E-09
7 BE -08
51E-06
3 OE-06
43E-O4
24E-10
4 1E-07
47E-04
33E-09
25E-08
45E-09
28E-10
16E^)5
3 8E-07
57E-10
30E-09
70E-O8
48E-14
1 9E-10
1 BE 09
2 OE-08
59E-07
59E-07
69E 09
3 OE-06
48E-07
1 3E 07
1 1E-08
Vogutt
Cone
mg/kgWW
30E -12
52E-11
35E-11
88E-12
1 2E-11
1 OE-10
1 9E-08
96E-12
45E-11
26E-10
1 4E-10
26E-10
60E-11
1 7E-10
1 3E-10
26E-11
1 5E-09
66E-10
43E-10
1 2E-08
5 1E-06
3 OE-06
4 3E-04
24E-10
4 1E-07
4 7E-04
33E-09
2 5E-08
45E-09
28E-10
1 6E-05
38E-07
57E-10
30E-09
7 OE-08
48E 14
t 9E'10
1 8E-0$
2 OE-08
59E-07
59E 07
69E-09
3 OE 06
4 BE 07
1 3E 07
1 IE OB
Cieam
Cone
mg/kgWW
3 BE 11
65E-10
4 3E-10
1 IE 10
15E-10
13E-09
2 3E 07
1 2E-10
56E-10
32E-09
1 7E-09
33E-09
74E-10
2 IE -09
1 7E-09
32E-10
1 9E-08
83E-09
54E^»
15E-07
51E-06
3 OE-06
4 3E 04
24E-10
4 1E 07
47E-04
33E-09
2 5E-08
45E-09
28E-10
16E-05
3 8E-07
57E 10
30E 09
7 OE-08
4 BE 14
1 9E-10
18E-09
20E 08
59E 07
59E 07
69E-09
30E 06
4 BE 07
1 3E 07
1 1F 08
Butter
Cone
mg/kgWW
1 2E-10
2 1E-09
1 4E-09
36E-10
5 1E-10
41E-09
7 6E-07
4 OE-10
1 8E-09
1 IE -08
57E-09
1 1E-08
24E-09
70E09
54E09
1 1E-09
6 3E-08
2 7E-08
1 BE 08
4 9E-07
51E-06
30E-O6
43E-04
24E-10
4 1E-07
4 7E-04
33E-09
2 5E-08
45E-09
28E-10
1 6E-05
38E437
57E-10
30E-09
7 OE-08
48E-14
1 9E-10
1 BE 09
2 OE-08
59E-07
59E 07
6 9E 09
3 OE-06
48E 07
1 3E 07
1 IF OB
E xposed
Produce
Cone
mg/kgWW
63E-14
1 IE 12
15E-12
4 7E-13
50E-13
25E-11
31E-09
9 1E-13
54E 12
73E-12
54E-12
1 2E 11
26E-12
86E-12
30E-11
25E-12
67E-10
1 7E-11
1 7E-11
45E-10
51E-08
2 5E 08
27E-05
42E^>7
22EX)9
52E-06
23E-11
25E-09
1 1E^>8
72E-11
1 3E 08
23E-09
26E 09
1 4E 08
70E 08
93E-12
9 IE O9
26E 10
2 1E 08
1 OE 05
1 OE 05
78E 09
4 IE 07
2 3E 08
8 5E 09
1 IF 06
Protected
Produce
Cone
mg/kgWW
48E-15
2 OE-14
3 BE 15
1 2E-14
39E-15
26E-14
27E-13
53E14.
1 OE 13
10E-13
1 1E-13
1 OE 13
26E 14
1 2E-I3
3 1E-13
39E-14
1 7E-13
1 5E-11
46E 12
23E 12
2 OE-10
97E-10
13E-11
75E-07
1 5E-10
2 OE-12
43E-13
43E-09
1 9E-08
1 2E-10
1 4E-10
1 BE 10
28E 09
93E-09
6 1E 08
24E-12
92E-09
16E-10
1 9E 08
1 BE 05
1 BE 05
1 2E 08
5 3E 07
34E 08
69E-10
? ?F 06
-------
TABLE 2  Maximum Modrlrd FrwimnfTientnl f *po«;urp Concentrations
Chemical
2,3.7.8 TCDD
1.2.3,7.8 PeCDD
1.2,3.4 7.8-HxCDD
1.2,3,6.7,8-HxCDD
1,2.3.7,8.9-HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2,3.7,8-PeCDF
2.3,4,7,8-PeCDF
1,2.3.4,7,B-HxCDF
1.2.3,6.7,8-HxCDF
1.2.3,7,8.9-HxCDF
2.3,4,6.7,B-HxCDF
1.2.3.4,6.7,8 HpCDF
1,2, 3,4. 7,8,9- HpCDF
OCDF
Telrachloroblphenyt
Hexachloroblphenyl
Heptachlorobiphenyl
Benzo(a)pyrene
Berwo(b)f1uof8nthene
Bl«(2-«thylhexy1)phthalate
Carbon tetrachtoride
Dibenz(a,h)anlhracene
Di(n)octyt phthalate
Heplachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachknocydopentadlene
Hexachtorophene
lndeno( 1 .2 ,3-cd)pyr ene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
?mc
Subarea
E3 max
E3 ma»
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
ESmax
E3 max
E3max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3max
E3 max
E3max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 max
E3 ma«
leafy
Produce
Cone
mg/kgWW
33E-12
59E-11
82E-11
22E-11
25E-11
1 3E-09
1 7E-07
4BE-11
29E-10
40E-10
2 7E-10
62E-10
1 4E-10
45E-10
1 4E-09
1 1E-10
3 7E-08
43E-10
7 BE 10
25E-08
28E-06
1 3E-06
1 5E-03
2 4E-07
32E-09
29E-04
1 3E-09
72E-09
70E-09
1 2E-10
1 8E-OB
32E-09
74E-09
3 2E-08
24E-07
1 7E-11
1 6E-08
33E-10
4 5E-08
33E-05
33E-05
54E-09
33E-07
4 8E-08 .
1 2E-08
1 2E-06
Pool
Produce
Cone
mg/kgWW
42E-15
1 7E-14
85E-15
9E-14
2E-14
1E-14
2E-13
3E-14
1E-13
1E-13
8E-13
7E-13
2E-14
1 9E-13
77E-13
96E-14
85E-13
1 1E-10
1 8E-11
1 1E-10
2 3E-11
1 1E-09
20E-11
8 BE -08
25E-10
21E-08
1 1E-11
1 OE-07
3 OE-08
14E-09
59E-08
27E-10
28E-12
28E-12
45E-11
1 7E-16
1 4E-11
83E-15
1 1E-11
28E-09
28E-09
23E-13
63E-11
34E-11
2 1E-14
28E-10
Rivet
Fish
Cone
mg/kg
68E-13
29E-12
4 IE 12
49E-12
3 1E-12
7 1E-12
53E-13
53E-12
24E-11
33E-11
45E-11
42E 11
1 OE-11
48E-11
52E-11
65E-12
22E-12
49E-10
4 4E-08
1 7E-08
7 1E-08
35E-07
5 OE-08
8 1E-10
3 1E-06
92E09
14E-09
83E-06
5 7E-07
66E-10
5 5E-08
39E-06
39E-12
36E-09
69E-10
19E-12
96E-09
34E-11
2 1E-08
1 OE-05
5 BE -05
60E-10
9 2E-08
69E-12
1 3E-08
44E-08
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg'L
40E-17
1 7E-16
39E-17
1 5E-16
92E-17
2 1E-16
32E-15
40E-16
99E-16
1 OE-15
1 3E-15
1 3E-15
31E-16
1 4E-15
3 OE-15
38E-16
80E-16
90E-14
74E-14
8 7E-14
1 2E-12
55E-12
25E-12
2 7E-11
23E-12
1 5E-13
28E-15
1 5E-11
1 8E-11
25E-13
1 1E-11
26E-12
39E-12
82E-11
1 7E-10
95E-14
43E-12
2 1E-12
1 3E-10
2 7E-09
2 7E-09
99E-12
1 2E 09
1 4E-11
1 1E-10
1 OE-10
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
8 2E-12
1 4E-10
95E-11
2 4E-M
34E 11
2 BE 10
5 1E-08
26E-11
1 2E-10
7 OE-10
38E-10
71E-10
1 6E-10
4 7E-10
36E-10
7 OE-11
42E-09
16E-09
1 1E-09
33E-08
21E-06
1 2E-08
1 7E-04
74E-11
1 BE-07
19E-04
13E-09
6 1E-09
91E-10
58E-11
7 1E-06
16E-07
79E-10
1 3E 08
42E-09
6 1E-12
43E-10
75E-10
2 7E-09
6 1E-08
6 1E-08
53E09
25E07
99E-09
2 7E 07
55E-09
Volume V, Appendix''
-------
                f    \
                \J
  TABIE 2  Maximum Modeled Fnvimnmrntal F«pn-;uir
Chemical
2,3.78-TCDD
1,2,3,7.8 PeCDD
1.2,3,4.7,8 HxCDD
1.2,3.6.7,8 HxCDD
1,2. 3. 7.8,9 HxCDD
1,2,3,4,6,7.8-HpCDD
OCDD
2.3.7.8TCDF
1,2,3,7,8-PeCDF
2,3.4, 7,8-PeCDF
t, 2,3,4, 7,8-HxCDF
1, 2,3.6. 7,8-HxCDF
1. 2,3.7,8,9 HxCDF
2.3,4,8,7,8-HxCDF
1.2.3,4,6,7.8 HpCDF
1, 2,3,4, 7,8,9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachloroblphenyl
Heptachloroblphenyl
Benzo(«)pyrene
Benzo(b)nuoranthene
Bls(2-«thy1nexyl)phthalate
Carbon letrachloride
Dfberu(a,h)anthracene
Dl(n)ocry) phlhalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachforoeyclopentadlene
HexacWorophene
lndeno( 1,2, 3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavaleni)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Z me
Subarea
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nt max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nl max
N1max
N1 max
N1 max
N1 max
Nl max
Nl max
Nl max
Nl max
N1 max
N1 max
N1 max
N1 max
N1 max
Nl max
Nl max
N1 max
N1 max
Nl max
N1 max
Nl max
1 cm Soil
Cone
mg/kg
36E-10
1 9E 09
23E 09
2 7E-09
3 OE-08
15E-07
32E-09
1 1E-08
1 4E-08
36E-O8
•a jcno
76E-09
38E^)8
2 3E-07
-1 nF-TW*
4 6E 07
3 7E-07
59E-07
5 BE 07
95E 06
35E-05
35E-06
20E-O5
25E-05
87E-07
1 7E-08
33E-05
90E-05
15E-06
6 8E-05
28E-05
4 7E-06
18E-04
2 2E-04
48E-07
27E-06
1 3E-05
BOE-04
1 7E-03
1 7E-03
1 9E-05
34E 03
1 7E-O5-
85E-04 '
1 2E-04
Beel
Cone
mg/kgWW
1 7E-10
29E 09
1 9E-09
Jc-10
72E-10
56E-O9
10E-06
53E-10
25E-09
14E-08
82E-09
34E-09
9 BE 09
79E-09
8 5E-08
3 7E-08
24E-08
66E-07
55E-05
32E-05
4 5E-03
23E-09
96E06
50E-03
3 5E-08
25E-07
46E-08
28E-09
3 8E-04
88E-06
4 IE-OS
7 OE-07
21E-07
38E-10
2 2E-08
4 8E-08
1 7E-07
1 5E-06
1 5E-06
2 9E-07
1 4E-05
5 2E-07
1 9E-05
32E-07
Pork
Cone
mg/kgWW
4 4E-11
56E 10
3 7E 10
1 5E-10
1 7E-10
1 OE 09
1 7E 07
12E 10
50E-10
28E 09
21E-09
3 IE -09
70E 10
23E 09
22E 09
5 4E-10
1 5£ 08
29E 08
1 7E 08
1 2E 07
36E 06
25E-06
29E-04
90E 10
1 1E 06
32E-04
25E-09
2 3E-07
5 2E-08
3 2E-09
24E-05
t2E06
1 7E-08
25E 07
99E 07
33E-10
1 OE-09
66E 08
50E 07
5 1E-06
5 1E-06
1 3E 06
36E 04
1 2E-08
8 1E 05
84E 08
Chicken
Cone
mg/kgWW
1 BE 12
89E 12
5 IE 12
79E 12
66E-12
• 1 2E-11
85E-11
34E 12
8 BE 12
47E 11
93E 11
7 4E-11
1 7E It
75E-11
1 OE-10
3 3E-11
1 OE 10
25E 09
1 4E 09
15E09
1 9E-10
86E 10
1 1E-11
40E 12
19E09
15E-11
48E 13
42E-10
10E 10
58E-12
3 6E 08
19E-09
1 3E 10
94E08
37E-10
1 3E 11
42E-09
74E 10
1 6E 05
96E 07
96E 07
20E 09
1 2E 05
1 4E 10
1 6E 05
73E 08
Egg
Cone
mgftgWW
2 4E -12
1 2E 11
70E 12
1 1E-11
91E-12
1 7E-11
1 2E-10
46E-12
1 2E-11
65E 11
1 3E 10
1 OE-10
23E 11
1 OE-10
1 4E-10
4 5E-11
1 4E-10
34E-09
20E09
20E09
2 4E-07
1 1E-06
1 36 08
50E 09
2 3E 06
1 9E 08
60E-10
52E07
1 2E-07
72E09
45E 05
24E06
15E09
1 2E-07
30E 07
15E-11
1 OE-10
12E09
1 6E-05
80E 08
80E 08
33E09
1 2E 05
28E 09
1 6E 05
73E 08
Milk
Cone
mg/kgWW
1 3E 11
22E 10
1 5E-10
40E-I1
55E-11
42E-10
7 6E 08
40E-11
1 9E 10
1 1E-09
62E-10
1 1E 09
25E-10
74E-10
6 OE-10
1 2E-10
84E-09
28E 09
18E 09
50E 08
22E-05
1 3E-05
18E-03
1 OE 09
38E-06
1 9E-03
1 4E-08
1 OE-07
1 9E-08
1 1E-09
1 5E 04
35E-06
51E-09
2 6E 08
63E07
43E-13
1 7E 09
1 7E 08
1 BE 07
24E-06
24E06
62E 08
27E 05
4 4E 06
1 2E 06
1 OE-07
Cheese
Cone
mg/kgWW
1 9E 10
32E 09
2 2E-09
6 OE-10
82E-10
64E09
1 1E 06
6 OE-10
28E-09
16E-08
93E-09
1 7E-08
38E-09
1 1E-08
90E-09
19E4J9
96E-08
42E08
27E-08
7 4E-07
22E-05
13E-05
18E-03
IDE -09
38E-08
1 9E-03
14E-08
1 OE-07
1 9E-08
1 1E-09
1 5E-04
35E-06
5 1E-09
26E-08
6 3E-07
43E-13
1 7E-09
1 7E-08
1 8E-07
24E 06
24E06
62E-08
2 7E-05
4 4E-06
1 2E-06
1 OE 07
Milk
Dessert
Cone
mg/kgWW
8 3E-11
1 4E 09
95E-10
26E-10
35E-10
2 BE 09
5 OE-07
26E-10
1 2E-09
70E-09
40E-09
72E-09
16E-09
48E-O9
39E-O9
8 OE-10
42E-08
1 8E-08
1 2E-08
32E-07
22E-05
1 3E-05
1 BE-O3
10E-09
3 BE -06
1 9E-03
1 4E-08
1 OE-07
19E-08
1 1E-09
15E^)4
35E-06
51E-09
26E-08
63E-07
43E 13
1 7E-09
1 7E-08
1 8E-07
2 4E 06
2 4E-06
6 2E 08
2 7E 05
4 4E 06
1 2E 06
1 OE 07
Yogurt
Cone
mg/kgWW
1 3E 11.
2 2E 10
1 5E-10
40E-11
55E-11
42E-10
76E 08
40E-11
1 9E-10
1 1E-09
62E-10
1 1E 09
25E-10
74E-10
6 OE-10
1 2E-10
64E 09
28E 09
18E-09
50E 08
22E-05
3E-05
BE-03
OE-09
BE 06
9E-03
4E-08
OE-07
9E-08
1E-09
5E-04
35E-06
5 1E-09
2 6E-08
6 3E-07
43E-13
1 7E-09
1 7E-08
1 8E 07
24E 06
2 4E 06
62E 08
2 7E05
44E 06
1 2E 06
1 Of! 07
Cream
Cone
mg/kgWW
1 6E 10
2 7E 09
1 8E-09
50E-10
68E-10
53E 09
96E-07
5 OE-10
24E-09
1 4E-08
77E-09
1 4E 08
32E-09
93E-09
75E-09
1 5E-09
8 OE-08
3 5E-08
2 2E-08
6 2E-07
22E-05
1 3E-05
1 8E 03
1 OE-09
38E-06
1 9E-03
1 4E-08
1 OE-07
1 9E-08
1 1E-09
1 5E-04
35E-06
51E09
2 6E 08
63E-07
43E-13
1 7E-09
1 7E 08
1 8E 07
2 4E 06
2 4E 06
62E 08
2 7E 05
4 4E 06
1 2E 06
1 OF 07
Butler
Cone
mg/kgWW
53E 10
B9E 09
6 OE-09
1 6E 09
22E 09
1 7E-08
31E-06
1 6E-09
77E-09
4 4E-08
2 5E 08
4 6E-08
1 OE-08
3 OE-08
2 5E-08
5 1E-09
26E-07
1 2E-07
7 3E 08
20E-06
22E-O5
3E-05
BE-03
OE-09
38E-06
9E 03
4E-08
OE^)7
9E-08
1E-09
5E-04
35E-06
51E^)9
26E-08
63E-07
43E-13
1 7E 09
1 7E 08
1 8E 07
24E 06
2 4E 06
62E 08
2 7E 05
44E 06
1 ?F 06
1 OF 07
Exposed
Produce
Cone
mg/kgWW
2 7E-13
46E 12
6 4E-12
23E 12
23E 12
1 OE-10
1 3E-08
38E-12
23E-11
31E-11
2 5E-11
51E 11
1 1E-11
39E-11
1 4E-10
1 3E-11
28E-09
72E-11
69E-11
1 9E-09
2 2E-07
1 OE 07
1 1E4)4
1 BE 06
2 IE 08
2 2E 05
97E 11
1 OE 08
4 5E 08
3 OE-10
1 2E 07
2 1E 08
2 4E 08
1 3E07
64E 07
82E 11
84E 08
2 3E 09
1 9E 07
4 3F 05
4 IE 05
7 4F 08
39F: 06
2 2E 07
75F 08
1 ?F 05
Protected
Produce
Cone
mg/kgWW
24E 14
1 3E 13
39P 1^
1 1E 13
3 BE 14
25E 13
27E 12
25E \\
59E 13
62E 13
98E-13
91E 13
21E 13
1 OE 12
2 8E-12
37E 13
1 7E 12
65E-11
19E 11
95E 12
1 2E 09
40E09
9 1E-11
3 1E 06
1 5E 09
83E 12
1 BE 12
1 8E 08
79E08
5 IE 10
1 4E 09
18E09
27E08
8 9E 08
58E 07
23E 11
89E 08
15E 09
1 8E 07
75E 05
75E 05
1 IE 07
5 1E 06
32E07
66E 09
2 1F 05
Volume V. Appendix V-11
-------
 TABLE 2  Maximum Modoird Environmental Exposure Concentrations
Chemical
2.3.7.8 TCDD
1,2,3,7,8-PeCDD
1,2,3.4,7,8 HxCDD
1, 2.3,6, 7.8-HxCDD
1,2,3,7,8,9 HxCDD
1,2,3,4,6,7,8 HpCDD
OCDD
2,3,7,8TCDF
1,2,3,7,8-PeCDF
2,3,4,7,8-PeCDF
,2,3.4,7.8-HxCDF
,2,3.6,7,8-HxCDF
.2.3,7,8.9 HxCDF
,3,4.6,7.8-HxCDF
,2,3,4,6.7,8-HpCDF
, 2,3,4, 7.8,9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachtofoblphenyl
Heptachkxoblphenyl
Benzo(i)pytene
Benzo(b)nuoranthene
Bl8(2-ethy1hexy1)phthalate
Carbon letrachlorlde
Dibenz(a,h)anlhracene
Di(n)octyt phthalale
HeptachkH
Hexachlorobenzene
Hexachtorobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno(1 ,2.3-cd)pyiene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromiurr (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nlmax
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Leafy
Produce
Cone
mg/kgWW
1 4E-11
24E-10
34E-10
92E-11
1 1E-10
55E-09
71E-07
2 OE-10
1 2E-09
16E-09
1 1E-09
25E-09
58E-10
1 8E-09
60E-O9
46E-10
15E-07
1 8E-O9
32E-09
1 OE-07
1 1E-05
55E-06
6 3E 03
97E-07
2 9E-O8
1 2E-03
53E-09
30E-08
29E-08
51E-10
1 7E-07
29E-08
70E-08
3 OE-07
23E-06
1 5E-10
1 5E-07
30E-09
4 2E-07
1 4E 04
1 4E 04
5 1E-08
30E 06
4 5E-07
1 1E-07
1 2E-05
Root
Produce
Cone
mg/kgWW
2 1E-14
1 16-13
72E-14
1 6E-13
1 2E-13
7 7E-13
52E-12
20E-13
59E-13
70E-13
1 6E-12
1 5E-12
33E-13
1 7E-12
70E 12
9 1E-13
85E-12
48E-10
7 4E 11
44E 10
1 4E-10
45E-09
1 4E-10
36E-07
25E-09
86E 08
44E-11
42E-07
1 3E-07
60E-09
59E-07
2 BE -09
27E-11
27E-11
44E-10
16E-15
1 3E-10
80E-14
1 OE-10
1 2E-08
1 2E-08
23E-12
6 1E-10
32E-10
'20E-13
27E-09
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
1 NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
35E-11
59E-10
4 OE-10
1 1E-10
1 *^F m
I 3C- IU
i *JF no
i f. c-uy
2 1E-07
1 1E-10
5 1E-10
29E-09
1 IF no
1 / C \JiJ
6 9E-10
_ — — -._
1 6E-09
3 3E-10
17E-08
69E-O9
44E-09
' 3E-07
B8E-08
51E-06
72E-04
3 1E-10
1 6E-08
79E-04
56E-09
25E-08
38E-09
2 4E-10
65E-05
15E-08
70E-09
1 1E-07
37E-08
54E-11
38E-09
66E-09
2 4E 08
2 5E-07
2 5E-07
4 7E 08
22E06
90E 08
25E-06
5 1E-08
Volume V, Appendix "
-------
TABLE 2  Maximum Modolrd Fiwimnmrnlnl f. «pnsmr Conrrntr,-ilirns
Chemical
2.3,7,8-TCDD
1.2.3.7.8-PeCDD
1,2,3,4,7.8 HxCDD
1,2.3.6,7.8-HxCDD
1,2,3,7,8,9 HxCOO
1,2.3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2.3,7,8-PeCDF
2,3,4, 7,8-PeCOF
1,2,3,4,7,8-HxCDF
1,2.3,6,7.8-HxCDF
1,2,3,7,8,9-HxCDF
2,3,4,6.7.a-HxCDF
1,2,3,4,8.7.8-HpCDF
1,2,3,4,7 89-HpCDF
OCDF
Tetiachlofoblphenyl
Hexachlorotiphenyl
Heptachkjroblphenyl
Benzo(a)pyrene
Benzo(b)nuoranthene
Bls(2-ethylhexy1)phlhalate
Carbon tetrachlorlde
Oibenz(a.h)anthracene
Di(n)octy) phthalate
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
1 ««*4
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
N2max
N2max
N2max
N2max
N2 max
N2 max
N2 max
N2max
N2 max
N2max
N2max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2max
N2 max
N2 max
N2max
N2 max
N2 max
N2max
N2 max
N2 max
N2max
N2 max
N2 max
N2max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2max
N2 max
1 cm Soil
Cone
mg/kg
1 2E-10
54E-10
55E-10
95E-10
6 1E-10
7 OE-09
33E-08
1 1E-09
33E-09
39E-09
86E-09
8 OE-09
9 1EO9
5 4E-08

1 OE-07
1 3E-07
2 1EO7
2 BE -06
1 3E-05
95E-07
75E-06
56E-06
32E-07
63E-09
12E-05
33E-05
54E-07
1 5E-05
64E-06
1 OE-06
40E-05
50E-05
1 1E-07
59E-07
28E-06
1 8E-04
62E-04
62E-04
4 1E-O6
76E-04
3 7E-06
1 9EO4
2 7E-05
Beef
Cone
mg/kgWW
62E-11
1 OE-09
7 1E-10
18E-10
26E-10
21E-09
37E-07
1 9E-10
91E-10
52E-09
29E-09
53E-09
1 2E-09
35E-09
2 ftp no
OC-vl*
31E-08
1 3E-08
87E-09
24E 07
20E-05
12E05
1 7E 03
84E-10
23E-06
1 8E 03
1 3E-08
93E-08
1 7E-08
1 OE-09
9 IE 05
21E-08
96E-09
1 7E-07
5 1E-08
89E-11
52E-09
1 1E-08
4 OE-08
57E-07
57E 07
69E-08
33E-06
1 2E-07
44E-06
72E-08
Pork
Cone
mg/kgWW
1 5E-11
20E-10
1 3E-10
46E-11
55E-11
37E-10
6 3E-08
43E-11
1 8E-10
1 OE-09
66E-10
10E-09
24E-10
74E-10
e ee in
D OC-10
ICC in
5C-10
5 4E-09
1 OE-08
64E-09
4 6E-08
13E-06
9 3E-07
1 1E-04
33E-10
26E-07
1 2E-04
93E-10
8 4E-OB
1 9E-08
1 2E-09
55E-06
26E-07
3 9E-09
5 5E-08
22E-07
74E-11
23E-10
1 5E-08
1 1E-07
1 9E 06
1 9E-06
3 OE-07
8 1E 05
27E09
1 BE 05
1 9E 08
Chicken
Cone
mg/kgWW
56E-13
25E 12
1 2E 12
1 BE 12
1 5E 12
> 2 BE 12
1 9E-11
1 1E-12
2 7E-12
1 4E-11
22E-11
1 BE 11
42E 12
1 8E 11
2 4E-1 1
7 5E-12
23E 11
89E 10
52E 10
54E-10
55E-11
32E-10
29E-12
15E-12
42E-10
56E 12
18E-13
1 5E-10
37E-11
21E 12
8 1E-09
44E-10
28E-11
2 1E-08
83E-11
2 BE 12
94E 10
1 6E-10
35E 06
35E 07
35E-07
45E-10
26E-06
3 1E-11
35E-06
1 6E 08
Egg
Cnnc
mg/kgWW
78E-13
34E 12
1 7E 12
25E-12
2 1E-12
3 BE 12
26E-11
1 6E-12
37E-12
19E-11
31E-11
24E 11
5BE-12
25E-11
3 4E-11
1 OE-11
31E-11
1 2E-09
72E-10
74E-10
69E 08
4 OE-07
36E-09
1 8E-O9
5 3E-07
7 OE-09
22E-10
1 9E 07
46E-08
2 7E-09
IDE 05
55E-07
33E-10
2 7E-08
6 6E-08
33E-12
22E-11
27E-10
35E-06
3 OE-08
3 OE-08
7 3E-10
26E-06
63E-10
35E-06
1 6E-08
Milk
Cone
mg/kgWW
4 7E 12
79E 11
53E 11
1 4E-11
1 9E-11
15E-10
2 8E-08
1 5E-11
69E-11
40E 10
22E-10
40E 10
92E 11
27E-10
2 1E-10
42E 11
23EO9
1 OE-09
66E 10
1 8E 08
79E-06
46E-06
65E-04
37E-10
92E-07
72E-04
51E-09
37E-08
68E-09
42E-10
3 6E-05
84E-07
12E-09
62E09
1 5E-07
10E 13
40E-10
3 BE 09
4 2E 08
90E 07
90E 07
1 5E 08
6 3E 06
1 OE-06
28E 07
24E 08
Cheese
Cone
mg/kgWW
70E 11
1 2E 09
80E 10
2 IE 10
29E-10
2 3E 09
4 2E-07
22E 10
1 OE-09
5 9E-09
33E-09
6 OE-09
1 4E-09
4 OE-09
3 1E-09
63E-10
35E-08
15E-08
99E-09
2 7E-07
79E-06
46E-06
65E-04
3 7E-10
92E-07
72E-04
51E-09
37E-O8
68E-09
42E-10
36E-05
84E-07
12E-09
62E-09
1 5E-07
1 OE-13
40E-10
38E-09
42E-08
9 OE-07
9 OE-07
1 5E-08
63E-06
1 OE-06
2 BE 07
24E 08
Milk
Dessert
Cone
mg'kgWW
30E-11
5 1E-10
35E-10
90E-11
1 3E-10
1 OE 09
1 8E-07
96E-11
45E-10
26E-09
1 4EO9
26E-09
60E-10
1 7E-09
1 4E-09
2 7E-10
15E-08
66E-09
43E-09
12E07
79E-O8
46E-O6
65E-04
3 7E-10
92E-07
72E-04
51E-09
37E-08
68E-09
42E-10
36E-05
84E-07
1 2E-09
62E-09
1 5E-07
1 OE-13
40E-10
3 BE 09
4 2E 08
90E 07
90E 07
1 5E 08
63E-06
1 OE 06
2 BE 07
2 4E 08
Yogurt
Cone
mg/kgWW
4 7E 12
79E-11
53E-11
1 4E-11
1 9E-11
1 5E-10
2 BE -08
15E-11
69E-11
40E-10
22E-10
40E-10
92E-11
27E-10
21E-10
42E-11
23E-09
IDE 09
66E-10
1 8E-08
79E-06
46E-06
6 5E-04
37E-10
9 2E-07
7 2E-04
51E-09
37E-08
68E-09
42E-10
36E-05
8 4E-07
12E-09
62E-09
1 5E-07
1 OE-13
38E 09
42E 08
90E 07
90E 07
1 5E 08
63E 06
1 OE 06
2 8E 07
?4E 08
Cream
Cone
mg/kgWW
58E-11
99E-10
6 7E-10
1 7E-10
24E-10
1 9E 09
3 5E-07
1 8E-10
86E-10
49E-09
2 7E-09
5 OE-09
1 1E-09
33E-09
26E-09
52E-10
2 9E 08
1 3E-08
82E-09
2 3E-07
79E-06
46E-06
6 5E-04
37E-10
9 2E-07
7 2E-04
5 IE 09
37E08
68E-09
42E-10
36E-05
8 4E-07
12E-09
62E 09
1 5E-07
10E 13
40E-10
3 BE 09
4 2E 08
90E 07
90E 07
1 5E 08
63E 06
1 OE 06
2 8E 07
? 4F 08
Butter
Cone
mg/kgWW
1 9E-10
32E-09
22E-09
57E-10
79E-10
63E-09
1 2E-06
60E-10
28E-09
1 6E-08
89E-09
1 7E-08
3 BE -09
1 1E-08
86E09
1 7E-09
96E-08
42E-08
2 7E 08
75E-07
79E-06
46E-06
65E-04
37E-10
9 2E 07
7 2E-04
51E09
37E-08
68E09
42E-10
84E-07
1 2E-09
62E-09
1 5E 07
1 OE 13
40E-10
38E 09
4 2E 08
90E 07
90E 07
1 5fT 08
63E 06
1 OE 06
2 8E 07
? 4F OB
Exposed
Produce
Cone
mg/kgWW
98E-14
1 7E-12
23E-12
76E 13
79E-13
38E-11
4 7E 09
1 4E-12
B3E-12
1 1E-11
87E-12
1 8E-11
4 1E-12
14E-11
4BE 11
41E-12
1 OEO9
26E-11
25E-11
69E-10
79E-08
38E-08
42E05
85E-07
50E 09
79E06
36E 11
39E09
1 7E08
1 1E 10
28E08
50EO9
55E09
3 OE-08
1 5E 07
1 9E 11
19E 08
55E 10
45E 08
1 6E 05
1 6E 05
1 7E 08
8 7E-07
4 8E 08
1 BE 08
2 RE 06
Protected
Produce
Cone
mg/kgWW
7 BE 15
36E 14
7 BE 15
26E 14
86E 15
57E 14
62E 13
84E-14"
18E 13
1 8E 13
23E 13
22E 13
52E 14
25E 13
67E 13
85E-14
3 BE 13
24E 11
7 IE 12
35E-12
35E-10
1 5E 09
25E-11
1 1E 06
33E-10
3 1E 12
66E 13
65E 09
29E 08
1 9E 10
31E 10
40E 10
60E 09
20E 08
1 3E 07
51E 12
20E 08
3 4E 10
4 1E 08
2 7E 05
2 7E 05
25E 08
1 IE 06
7 2E 08
1 5E 09
4 8F 06
-------
TABLE 2  Maximum Mndrtpfl F nvironnirn(,i) F»poMjrp Cnnr
Chemical
2,3.7.8 TCDD
1,2,3.7,8 PeCDD
1.2,3.4.7.BHxCOD
1,2,3.6,7,8-H«CDD
1 2,3.7,8,9 HxCDD
1,2.3,4,6,7,8-HpCDD
OCDD
2,3.7,8-TCDF
1,2,3.7,8-PeCDF
2,3,4.7,8-PeCDF
1, 2,3,4, 7.8-HxCDF
1.2,3.6,7.8-HxCDF
1,2,3,7,8,9-HxCDF
2,3.4,6,7,8 HxCDF
1, 2,3,4,6. 7,8-HpCDF
1,2,3,4,7,8.9 HpCOF
OCDF
Tetrachloroblphenyl
Hexachtoroblphenyl
Heptachtorobiphenyl
Benzo(a)pyrene
Benzo(b)fluoranthene
Bis(2-e1hy1hexyl)phthalale
Carbon tetrachloride
Dibenz(a,h)anthracene
Di(n)octyl phlhalate
Heptachlor
Hexachtorobenzene
Hexachkxobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver .
Thallium
Zinc
Subarea
N2 max
N2max
N2 max
N2 max
N2max
N2 max
N2max
N2max
N2max
N2max
N2 max
N2max
N2 max
N2max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2max
N2 max
N2max
N2max
N2 max
N2max
N2 max
N2max
N2 max
N2 max
N2max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
N2 max
Leafy
Produce
Cone
mg/kgWW
50E-12
90E-11
1 2E-10
34E-11
39E-11
20E-09
2 6E-07
74E-11
45E-10
60E-10
41E-10
94E-10
2 1E-10
68E-10
2 2E-09
1 7E-10
5 6E-08
66E-10
1 2E 09
3 8E-08
4 2E-06
20E-06
2 3E-03
36E-07
7 1E-09
44E-O4
20E-09
1 1E-08
1 IE-OS
1 9E-10
4 IE-OS
7 1E-O9
1 6E-08
6 9E-08
5 2E-07
35E-11
35E-08
70E-10
9 6E-08
5 OE-05
5 OE-05
1 2E-08
70E 07
1 OE-07
2 5E-08
26E-06
Root
Pioduce
Cone
mg'kgvVW
69E 15
32E-14
1 BE 14
4 2E 14
2 7E-14
18E-13
12E-12
6BE-14
1 8E-13
20E-13
38E-13
35E-13
83E-14
40E 13
1 7E-12
2 IE 13
1 9E-12
1 7E 10
2 7E-11
1 6E 10
4 1E-11
1 7E-09
3 BE 11
1 3E-07
5 7E-10
32E-08
16E-11
1 5E-07
46E-08
22E-09
1 3E-07
62E-10
60E-12
59E-12
97E-11
35E-16
29E-11
18E-14
23E-11
4 3E-09
43E-09
50E-13
1 3E-10
72E-11
4 4E-14
60E-10
River
Fish
Cone
mg/kg
59E 12
27E-11
1 4E-11
2 5E 11
1 6E 11
23E-11
22E-12
53E-11
1 7E-10
21E-10
22E-10
2 1E-10
49E-11
2 3E-10
1 8E-10
23E-11
68E-12
1 BE 08
32E 07
2 1E 07
3 BE 07
72E-06
7 7E-08
3 4E-08
37E-05
36E 07
5 5E-08
3 4E-04
23E-05
2 7E-08
1 7E-06
48E-05
2 OE-10
2 OE-07
3 6E-08
1 OE-10
3 2E-07
1 BE -09
1 1E-06
4 3E-04
2 4E-03
33E-08
50E 06
35E-10
6 7E 07
2 2E 06
take
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Rivrr
Water
Cone
mg'L
35E-16
1 6E 15
1 4E 16
7 3E-16
4 6E 16
6 7E-16
1 3E 14
40E-15
73E-15
67E-15
65E-15
6 1E-15
1 4E-15
69E-15
1 OE-14
1 3E-15
25E-15
32E 12
55E-13
1 1E-12
6 7E-12
1 1E 10
3BE-12
1 1E-09
27E-11
58E 12
1 1E-13
62E-10
73E-10
1 OE-11
33E-10
3 1E-11
2 OE-10
45E-09
90E-09
52E-12
1 4E-10
1 1E-10
69E-09
1 1E-07
1 tE-07
54E-10
65E 08
7 1E-10
56E 09
5 1E 09
lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
1 3E 11
2 2E 10
1 5E-10
3 BE 11
5 3E 11
42E 10
7 7E-08
4 OE-11
1 9E-10
1 1E-09
59E-10
1 1E-09
25E-10
72E-10
57E-10
1 1E-10
64E-O9
25E-09
1 6E-09
50E-08
32E-06
1 9E-06
26E-04
1 1E-10
39E-07
29E-04
20E-09
93E-09
1 4E-09
88E-11
16E-05
36E-07
1 7E-09
2 7E-08
8 8E-09
1 3E-11
91E-10
1 6E-09
5 6E-09
9 3E-08
9 3E 08
1 1E-08
52E-07
2 1E-08
58E 07
1 2E-08
Volume V. Appendix/' " \
-------
  TAB! E 2  MaximutrTModrlrd Environnirnlal Exposure Concentrations
Chemical
2,3,7.8-TCDD
1.2.3,7.8 PeCDD
1.2,3.4, 7. 8-HxCDO
1,2,3,6,7,3 HxCDD
1.2,3, 7,8,9 HxCDD
1, 2,3,4,6. 7,8-HpCDD
OCDD
2,3.7,8-TCDF
1,2,3,7,8-PeCDF
2,3,4, 7,8-PeCDF
1, 2.3,4, 7.8-HxCDF
1.2,3,6,7,8-HxCDF
1,2,3,7.8.9-HxCDF
2,3,4,6.7 8-HxCDF
1,2.3.4,6,7.8-HpCDF
1,2,3,4.7,8.9 HpCDF
OCDF
Te(rachlorobipheny)
Hexachloroblphenyl
Heptachloroblpbenyl
Benzo(a)pyrene
Benzo(b) nuoranlhene
Bis(2-ethylhexyl)phthalate
Carbon tetrachtoride
Dibenz(a ,h)anthr acene
Dl(n)octy1 phlhalale
Heptachlor
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver .
Thallium
Zinc
Subaiea
N3ma»
N3 max
N3max
N3 max
N3max
N3 max
N3 max
N3max
N3max
N3max
N3max
N3max
N3 max
M3 max
N3 max
N3max
N3 max
N3max
N3 max
N3 max
N3 max
N3max
N3max
N3 max
N3 max
N3max
N3max
N3 max
N3max
N3max
N3 max
N3 max
N3 max
N3max
N3max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3max
N3 max
N3 max
N3 max
N3 max
1 cm Soil
Cone
mg/kg
33E-11
1 6E-10
1 7E-10
30E-10
1 9E-10
22E-09
1 1E-08
30E-10
95E-10
1 2E-09
27E-09
25E-09
58E-10
j DC no
1 7F nn
22E-09
3 3E-08
36E-08
59E-08
58E-08
80E 07
35E-06
2 8E-07
20E-06
1 8E-06
8 7E-08
1 7E-09
33E-06
90E-06
1 5E-07
49E-06
20E-06
3 7E-07
14E-05
1 7E-05
3 8E-08
2 1E-07
9 9E-07
62E-05
1 7E-04
1 7E-04
1 4E-06
2 7E-04
1 3E-06
66E-05
93E-06
Beef
Cone
mg/kgWW
1 7E 11
28E-10
19E-10
5 1E-11
70E-11
56E-10
1 OE-07
53E-11
25E-10
1 4E-09
79E-10
1 5E-09
33E-10

1 5E-10
84E 09
3 7E-09
24E-09
66E 08
54E 06
32E 06
4 5E 04
23E-10
72E-07
50E-04
35E-09
2 5E-08
46E-09
28E-10
2 9E-05
6 7E-07
33E-09
5 7E-08
1 7E 08
31E-11
1 8E-09
39E-09
1 4E-08
1 5E-07
1 5E-07
2 4E-08
1 1E-06
4 2E-08
1 5E-06
25E-08
Pork
Cone
mg'kgWW
4 3E 12
54E 11
35E 11
1 3E 11
16E 11
1 OE-10
1 7E-08
1 2E 11
48E-11
2 7E-10
1 9E-10
29E-10
66E 11
2 1E-10
1 9E 10
45E-11
1 5E-09
29EX)9
1 7E 09
1 2E-08
3 5E 07
25E47
29E-05
90E-11
82E-08
32E 05
25E 10
2 3E-08
52E-09
32E 10
1 7E-06
8 4E 08
1 3E 09
1 9E 08
7 8E-08
26E-11
80E 11
51E-09
39E 08
5 1E 07
5 1E 07
1 OE-07
2 BE 05
93E 10
63E06
65E 09
Chicken
Cone
mg/kgWW
1 6E 13
7 4E 13
3 BE 13
5 BE 13
4 7E 13
87E 13
6 1E 12
32E-13
77E-13
40E 12
69E 12
55E 12
1 3E 12
56E-12
7 7E-12
24E 12
72E-12
24E-10
1 4E 10
15E-10
16E 11
86E-11
86E 13
40E 13
1 3E-10
15E-12
4 BE 14
42E-11
1 OE-11
58E-13
26E-09
14E-10
98E 12
73E 09
29E 11
1 OE-12
33E-10
58E-11
1 2E 06
96E 08
96E-08
1 6E 10
92E 07
1 1E-11
1 2E 06
57E 09
Egg
Cone
mg'kgWW
2 2E 13
1 OE 12
53E 13
80E 13
66E 13
1 2E 12
84E 12
44E 13
1 IE 12
55E-12
95E 12
76E 12
1 BE 12
7 7E 12
1 1E-11
33E 12
99E 12
34E-10
20E 10
20E 10
2 OE-08
1 1E 07
1 IE 09
50E 10
1 7E 07
1 9E 09
60E-11
52E08
1 2E 08
72E-10
32E-06
1 7E-07
1 1E-10
95E09
2 3E-08
1 2E-12
78E-12
94E 11
1 2E 06
80E 09
80E 09
26E 10
92E-07
22E-10
1 2E 06
5 7E 09
Milk
Cone
mg/kgWW
1 3E 12
2 1E 11
1 4E 11
3 BE 12
53E 12
4 2E 11
76E 09
4 OE-12
1 9E 11
1 1E-10
60E 11
1 1E-10
25E-11
73E 11
58E-11
1 2E-11
64E-10
28E-10
1 BE-10
50E-09
2 1E^)6
3E-06
8E-04
OE-10
9E-07
9E-04
4E-09
OE-08
9E-09
1 1E-10
1 1E-05
2 6E-07
41E-10
2 1E-09
5 1E-08
35E 14
1 4E-10
1 3E 09
1 4E 08
24E 07
24E 07
50E-09
22E-06
3 5E-07
96E 08
82E 09
Cheese
Cone
mg/kgWW
1 9E 11
3 2E 10
2 2E 10
5 7E-11
80E 11
63E-10
1 IE 07
6 OE-11
28E-10
16E-09
9 OE-10
16E-09
37E-10
1 1E-09
86E-10
1 7E-10
96E-09
42E-09
27E-09
74E-08
21E-06
13E-08
1 8E-04
1 OE-10
29E-07
1 9E-04
14E-09
1 OE-08
1 9E-09
1 1E-10
1 IE-OS
2 6E-07
41E-10
21E-09
5 1E-08
35E-14
1 4E-10
1 3E-09
1 4E-08
24E-07
24E-07
50E-09
22E 06
3 5E-07
96E-08
82E 09
Milk
Dcsseit
Cone
mg'kgWW
8 3E 12
1 4E-10
9 4E 11
25E 11
34E-11
2 7E 10
5 OE 08
26E-11
1 2E-10
7 OE-10
39E-10
7 1E-10
1 6E-10
4 7E-10
37E-10
75E-11
4 1E-09
1 8E-09
1 2E-09
32E-08
21E-06
1 3E-06
1 BE -04
1 OE-10
29E-07
1 9E-04
14E-09
10E^)8
1 9E-09
1 1E-10
1 IE-OS
26E-07
4 1E-10
2 1E-09
51E-08
35E-14
1 4E-10
1 3E-09
1 4E-08
24E 07
2 4E 07
5 OE 09
22E 06
35E 07
96E-08
82E-09
Yogurt
Cone
mg/VgWW
1 3E-12
2 1E-11
1 4E-11
3BE-12
53E-12
42E-11
76E-09
4 OE-12
1 9E-11
1 1E-10
6 OE-11
1 1E-10
25E-11
73E-11
58E-11
1 2E-11
64E-10
28E-10
1 8E-10
50E-09
21E-06
13E-06
1 BE -04
1 OE-10
29E-07
19E^)4
14E-09
1 OE-08
1 9E-O9
1 1E-10
1 1Efl5
26E-07
4 1E-10
2 1E-09
5 1E08
35E-14
1 4E-10
1 3E-09"
1 4EflB
2 4E-07
2 4E O7
50E^9
2 2E06
35E07
96EOB
8 2E-09
Cream
Cone
mg/kgWW
1 6E-11
2 7E-10
1 8E-10
4BE-11
66E-11
53E-10
9 6E-08
50E-11
23E-10
1 3E-09
75E-10
1 4E-09
3 1E-10
91E-10
72E-10
1 5E-10
80E-09
35E-09
22E09
6 2E-08
2 1E-06
1 3E-06
1 BE 04
1 OE-10
29E-07
1 9E-04
14E-09
1 OE^)8
1 9E-09
1 1E-10
1 1E-05
26E-07
4 1E-10
2 1E^)9
5 1E-08
35E-14
1 4E-10
1 3E-09
1 4E-08
24E 07
2 4E 07
50E 09
2 2E 06
35E07
96E 08
B 7F 09
Butler
Cone
mg/kgWW
52E-11
BBE-10
59E 10
1 6E-10
22E-10
1 7E-09
3 1E-07
1 6E-10
77E-10
44E-09
24E-09
45E-09
1 OE-09
30E-09
24E-09
48E-10
26E-08
1 1E-08
73E09
2 OE-07
21E-06
1 3E-06
18E-04
1 OE-10
2 9E-07
1 9E-04
14E-09
1 OE-08
1 9E-09
1 1E-10
1 IE-OS
26E-07
4 1E-10
21E-09
51E-08
35E-14
1 4E 10
13E09
1 4E 08
24E 07
2 4E 07
5 OE 09
22E 06
35E 07
9 6E 08
fl 2E 09
Exposed
Produce
Cone
mg/kgWW
2 7E-14
46E-13
63E 13
21E-13
22E-13
1 OE-11
1 3E^9
38E-13
23E-12
31E-12
24E-12
49E 12
1 1E-12
37E-12
1 3E-11
1 2E 12
28E-10
7 1E-12
69E-12
1 9E-10
22E4W
1 OE 08
1 IE 05
1 BE -07
1 6E-09
22E-06
97E 12
1 OE-09
45E-09
30E 11
88E 09
16E-09
19E09
1 OE08
5 1E 08
67E 12
6 7E 09
1 9E 10
1 5E 08
4 3E 06
4 3E 06
5 BE 09
30E 07
1 7E 08
6 1E 09
9 7F 07
Protected
Produce
Cone
mg/kgWW
22E 15
1 OE 14
24E 15
82E 15
2 7E 15
1 8E-14
20E 13
23E-H
51E-14
52E 14
73E 14
6 BE 14
1 6E 14
77E 14
21E 13
27E 14
12E 13
64E-12
19E -r
95E 13
10E 10
40E 10
73E 12
3 1E 07
1 IE 10
83E-13
18E 13
1 BE 09
79E 09
5 1E-11
97E 11
1 3E 10
2 1E 09
69E 09
45E08
1BE 12
69E 09
1 2E 10
1 4E 08
75E 06
75E 06
8 7F 09
39E 07
25E 08
5 1E 10
1 7F 06
Volume V, Appendix V-11
-------
TABLE 2  Maximum Modeled Fnvironmrntal Exposure Concentrations
Chemical
2.3.7.8-TCOD
1.2,3,7,8-PeCDD
1,2,3,4,7,8-HxCDD
t,2.3,6,7,8-HxCDD
1,2,3,7,8,9-HxCDD
1,2,3,4,6,7,8-HpCDO
OCDD
2,3,7,8-TCDF
1,2.3,7,8-PeCDF
2,3,4, 7,8-PeCOF
1 2,3,4,7.8-HxCDF
1,2.3,6.7.8-HxCDF
1,2.3,7,8.9-HxCDF
2,3,4,6.7,8 HxCDF
1.2,3.4,8,7,8-HpCOF
1, 2.3,4, 7,8,9-HpCDF
OCDF
Tetrachtoroblphenyl
Hexachtoroblphenyl
Heptachtoroblphenyl
8en20(a)pyreTW
Benzo(b)nuoranthene
Bls(2-ethy1hexyt)phthalate
Carbon letrachloride
Dibenz(a,h)anthracene
Di(n)octyt phthalate
Heptachlor •
Hexachkxobenzene
Hexachtofobutadiene
Hexachtofocyctopentadiene
Hexachtorophene
lndeno(1 ,2.3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3 max
N3max
N3max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3 max
N3max
N3 max
N3 max
N3 max
N3 max
N3max
N3 mat
N3 max
Leafy
Produce
Cone
mg/kgWW
1 3E-12
24E-11
34E-11
92E-12
1 1E-11
55E-10
7 1E-08
20E-11
1 2E-10
1 6E-10
1 1E-10
25E-10
58E-1t
1 8E-10
60E-10
46E-11
1 5E-08
1 8E-10
32E-10
1 OE-08
1 1E-06
5 5E-07
63E-04
97E-08
22E-09
12E-04
53E-10
30E-09
29E-09
51E-11
1 3E-08
22E-09
55E-09
2 4E-08
1 BE-07
12E-11
1 2E-08
24E-10
3 3E-08
1 4E-05
1 4E-05
40E-09
24E-07
3 5E-08
87E-09
9 IE -07
Root
Produce
Cone
mg/kgWW
20E-15
93E-15
54E-15
1 3E-14
84E-15
56E-14
3 7E-13
1 9E-14
52E-14
59E-14
1 2E-13
1 1E-13
25E-14
12E-13
52E-13
66E-14
61E-13
48E-11
74E 12
44E-11
1 2E 11
45E-10
1 1E-11
36E-08
1 8E-10
B6E 09
44E-12
42E-08
13E-08
60E-10
4 2E-OB
20E-10
21E-12
21E-12
34E-11
1 2E-16
10E-11
62E-15
79E-12
1 2E-09
1 2E-09
1 7E-13
4 7E-11
- 25E-11
1 5E-14
21E-10
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
34E 12
58E-11
39E-11
1 OE-1,1
14E-T1
1 1E-10
2 1E-08
1 1E-11
5 1E-11
29E-10
1 6E-10
30E-10
68E-11
20E-10
1 6E-10
31E-11
1 7E-09
68E-10
44E-10
1 3E-08
87E-07
51E-07
72E-05
3 1E-11
12E-07
79E-05
56E-10
25E-09
38E-10
24E-11
50E-06
1 1E-07
57E-10
94E-09
30E-09
44E-12
3 1E-10
54E-10
1 9E-09
2 5E-08
2 5E 08
38E-09
1 8E 07
7 2E 09
20E-07
40E 09
Volume V, Appendix y
-------
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-------
TABLE 2  Maximum Modrlod Fnvimnmrntal Fxposuro Concentrations
Chemical
2,3.7.8 TCDD
1,2,3.7.8-PeCDD
1. 2,3.4, 7.8-HxCDD
1,2.3.6,7,8-HxCDD
1,2,3,7.8,9-HxCDD
1.2,3,4,6,7,8-HpCDD
OCDD
2,3.7.8-TCDF
1,2.3.7,8 P«COF
2,3.4,7,8-PeCDF
1, 2,3,4, 7,8-HxCDF
1, 2.3,6, 7.8-HxCDF
1,2,3.7,8,9-HxCDF
2.3.4.6,7,8-HxCOF
1,2,3,4,6,7,8-HpCDF
1, 2,3.4, 7,8.9-HpCDF
OCDF
Tetrachloroblphenyl
Hexachtoroblphenyt
Heptachloroblphenyt
Benzo(a)pyren«
Beruo(b)fluoranthene
Bl»(2-ethythexy<)phthalate
Carbon letrachlorlde
CHbenz(a ,h)anthracene
Dt(n)octy1 phlhalale
Heptachlor
Hwcachtorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
SI max
SI max
SI max
S1 max
St max
St max
SI max
51 max
S1 max
SI max
SI max
SI max
S1 max
S1 max
S1 max
SI max
S1 max
SI max
S1 max
S1 max
SI max
51 max
51 max
S1 max
St max
SI max
SI max
SI max
SI max
SI max
St max
St max
S1 max
S1 max
St max
St max
SI max
SI max
S1 max
St max
SI max
SI max
S1 max
S1 max
S1 max
St max
Leafy
Produce
Cone
mg/kgWW
18E-11
33E-10
46E-10
1 2E-10
1 4E-10
74E-09
95E-O7
2 7E-10
16E-09
22E-09
1 5E-O9
34E-09
78E-10
25E09
8 1E-O9
62E-10
20E-07
24EO9
4 3E-09
1 4E07
1 5E-05
74E-06
84E-O3
1 3E^)6
31E-08
1 6E-03
7 1E-09
40E-08
39E-08
68E-10
18E-07
32E-08
79E-08
34E-07
26E-06
7E-10
7E-07
4E-09
BE-07
BE -04
8E-04
58E-08
35E-06
5 1E-07
1 2E-07
1 3E-05
Root
Produce
Cone
mg/kgWW
2 7E-14
1 3E-13
7BE-14
19E-13
1 2E-13
82E 13
55E-12
26E-13
72E-13
82E-13
1 7E-12
16E-12
37E-13
18E-12
75E-12
96E-13
89E-12
64E 10
t OE-10
59E-10
1 7E-10
60E-09
1 6E-10
49E-07
26E-09
1 2E-07
59E-11
56E-07
1 7E-07
80E-09
62E-07
29E-09
31E-11
30E-11
49E-10
8E-15
5E-10
90E-14
2E-10
6E-08
6E-08
25E-12
69E-10
37E-10
22E-13
3 OE-09
River
Fish
Cone
mg/kg
1 4E-11
64E-11
99E 11
1 2E-10
77E-11
1 8E-10
1 3E-11
1 1E-10
5 OE-10
73E-10
1 1E-09
1 OE-09
24E-10
1 2E-09
t 3E-09
16E-10
55E-11
98E-09
8 7E-07
3 4E-07
1 4E-06
70E-06
84E-07
1 6E 08
71E05
1 8E-07
2 BE 08
1 6E-04
1 1E-05
t 3E-08
1 1E-06
89E-05
90E-11
8 7E-08
1 6E-08
46E-11
1 9E-07
82E-10
50E-07
2 OE-04
1 2E-03
1 4E 08
22E-06
1 6E-10
31E-07
1 OE 06
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
83E-16
3 7E-15
93E-16
36E-15
23E-15
51E-15
79E-14
81E-15
21E-14
23E-14
32E-14
30E-14
72E-15
34E-14
74E-14
94E-15
20E 14
1 8E-12
15E-12
1 7E-12
24E-11
1 1E-10
4 1E-11
53E-10
52E-11
29E-12
55E-14
3 OE-10
35E-10
50E-12
23E-10
58E-11
90E-11
2 OE-09
41E-09
23E-12
85E-11
5 1E-11
3 1E 09
54E 08
5 4E-08
24E-10
29E 08
32E 10
2 6E-09
23E-09
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
46E-11
79E-10
53E-10
1 4E-10
1 9E-10
1 5E-09
28E-07
1 5E-10
68E-10
39E-09
22E-09
4 OE-09
9 1E-10
27E-09
21E-09
43E-10
23E-08
91E-09
59E-09
18E-07
12E-05
68E-06
96E-04
4 1E-10
1 7E-06
1 1E-03
75E-09
34E-08
51E^»
3 2E-10
70E-05
16E-06
81E-09
13E4J7
43E-08
62E-11
44E-09
76E-09
27E-08
34E-07
3 4E-07
54E-08
25E-06
1 OE-07
28E-06
5 7E-08
Volume V, Appendix
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-------
TABLE 2  Maximum Modeled Environmental Fnposurp Concentrations
Chemical
2,3.7,8-TCDD
1.2.3.7.8 PeCDD
1.2.3,4,7.8-HxCDD
1,2,3.6,7,8 HxCDD
1.2,3.7.8.9-HxCDD
1,2,3,4,6,7.8-HpCDD
OCDD
2,3,7,8-TCDF
1.2.3.7,8-PeCDF
2.3,4,7,8-PeCDF
1, 2,3,4, 7,8-HxCDF
1,2,3,6.7,8-HxCOF
1,2,3.7.8,9-HxCDF
2.3,4.6,7.8-HxCDF
1.2.3.4,6.7.8 HpCDF
1,2.3.4.7.8.9 HpCDF
OCDF
Tetrachloroblphenyl
Hexachtoroblphenyt
Heptachloroblphenyl
Benzo(a)pyrene
Benzo(b)nuoranlhene
Bl«(2-ethyfhexy1)phthata1e
Carbon letrachloride
Dlbenz(a,h)anthracene
Dl(n)octyt phthalate
Heptachlor
Hexachlorob«nzene
Hexachtorobuladtene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno( 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavatent)
Lead
Mercury
Mercury (methyl BCD
Nickel
Selenium
Silver .
Thallium
Zinc
Subarea
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2max
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
52 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
S2max
S2 max
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 rna«
Leafy
Produce
Cone
mg/kgWW
50E-12
90E 11
1 2E-10
34E-11
39E-11
20E-09
2 6E-07
74E-11
4 5E-10
60E-10
4 1E-10
94E-10
2 1E-10
68E-10
22E-09
1 7E-10
56E-08
65E-10
1 2E-09
3 BE -08
42E 06
2 OE-06
2 3E 03
36E-07
44E-09
44E-04
20E-09
1 1E-08
1 1E-08
1 9E-10
26E-08
45E-09
1 1E-08
46E-08
35E-07
23E-11
23E-08
4 7E-10
64E-08
50E-05
50E-05
77E-09
4 7E-07
6 BE -08
1 7E-08
1 7E-06
Root
Produce
Cone
mg/kgWW
64E 15
26E-14
1 2E-14
2 BE 14
1 7E-14
1 1E-13
73E-13
65E-14
1 6E-13
1 7E-13
26E-13
24E-13
60E-14
27E-13
1 1E-12
1 4E-13
1 2E-12
1 7E-10
2 7E-11
1 6E-10
35E-11
1 6E-Q9
30E-11
1 3E 07
35E-10
32E-Q8
1 6E-11
1 5E-07
46E-08
22E-O9
82E-08
39E-10
40E-12
40E-12
65E-11
24E-16
20E-11
12E-14
1 5E-11
43E-09
43E-09
34E-13
90E-11
48E-11
29E-14
40E-10
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA.
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg'kgWW
1 2E 11
2 1E 10
1 4E-10
36E-11
5 1E-11
42E-10
7 7E-08
40E-11
1 9E-10
1 1E-09
57E-10
1 1E-09
25E-10
7 1E-10
54E-10
1 1E-10
64E-09
25E-09
16E-09
50E-08
32E-06
19E-06
26E-04
1 1E-10
25E-07
29E-04
20E-09
93E-09
14E-09
B8E-11
99E-06
22E-07
1 1E-09
1 8E-08
59E-09
87E-12
6 1E-10
1 1E-09
38E-09
9 3E-08
9 3E-08
76E 09
35E 07
1 4E 08
39E 07
7 8E-09
Volume V. Appendix7
-------
TABLE 2  Maximum Modeled Environmental Exposure Concentrations
        Chemical
                                                                                      Milk                                     Exposed   Protected
           1 cm Soil     Beel       Pork     Chicken      Egg       Milk     Cheese    Dessert     Yogurt     Cteam      Butter     Produce   Produce
Subarea      Cone       Cone       Cone      Cone      Cone      Cone      Cone      Cone      Cone      Cone      Cone      Cone       Cone
             mg/kg    mg/kgWW mg/kgWW  mg/kgWW mg/kgWW  mg/VgVVW  mg/kgWW  mg/kgWW  mg/kgWW  mg/kgWW  mg/kgWW  mg/kgWW mg/kgWW
2.3.7.8 TCDD
1.2. 3,7.8 PeCDD
1,2.3.4.7.8 HxCDD
1,2. 3,6,7. 8-HxCDD
1.2,3,7,8,9-HxCDD
1,2.3,4,6.7.8-HpCDD
OCDD
2,3.7,8-TCDF
1.2,3,7,8-PeCDF
2.3,4, 7,8-PeCDF
1,2.3,4.7,8-HxCDF
1,2,3,6.7,8-HxCDF
1.2,3,7,8.9-HxCDF
23,4.6,7,8-HxCDF
1 23.4,6,7,8 HpCDF
1,2.3,4,7,8,9 HpCDF
OCOF
Tetrachlorobiphenyl
Hexachlorobiphenyl
Heptachtoroblphenyl
Benzo(a)pyrene
Benzo(b)riuoranthene
Bl*(2-«thythexy1)phthalate
Carbon tetrachtoride
Olbenz(a,h)anthracene
Dt(n)octy1 phthalate
Heptachkx
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopenladlene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
ThalliurVi
Zinc
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
33E-11
1 3E-10
1 2E-10
20E-10
1 2E-10
1 4E-09
65E-09
31E-10
88E-10
OE-09
8E-09
7E-09
2E-10
9E-09
1E-08
4E-09
20E-08
39E 08
65E-08
64EO8
7 1E-07
39E-06
23E-07
22E^>6
1 1E-06
9SE-08
19E-09
36E-06
99E-06
1 6E-07
30E-06
1 2E-06
22E-07
85E-06
1 OE-05
23E-08
1 2E-07
59E-07
3 7E-05
1 9E-04
1 9E-04
8 7E-07
1 6E-04
79E-07
39E-05
56E-06
18E 11
3 IE-Id
2 1E-10
53E-11
75E-11
6 1E-10
1 1E-07
58E-11
27E-10
16E-09
84E-10
16E-09
36E-10
1 OE-09
80E-10
1 6E-10
93E-09
4 OE-09
26E 09
73E-08
60E-06
35E-06
50E04
25E-10
45E 07
55E-04
39E-09
28E-08
5 OE-09
31E-10
1 BE-05
4 1E-07
20E09
35E-08
1 1E-08
19E-11
1 1E-09
24E-09
84E-09
1 7E-07
1 7E-07
1 4E-08
70E07
26E-08
9 3E-07
1 5E 08
45E-12
58E 11
3 7E 11
2E-11
5E-11
1E-10
9E-08
3E-11
52E-11
29E-10
1 8E-10
30E-10
68E-11
2 1E 10
1 8E-10
39E-11
1 6E^9
3 1E-09
1 9E-09
1 4E-08
39E-07
28E-07
32E05
1 OE-10
50E-08
35E415
28E-10
25E-08
5 7E-09
35E 10
1 1E-06
5 IE-OS
81E-10
12E-08
4 7E-08
1 6E-11
49E-11
3 1E4J9
23E 08
56E-07
56E-07
62E-08
1 7E-05
56E-10
38E-06
39E-09
1 6E 13
62E 13
26E 13
3 8E-13
30E-13
55E-13
' 37E-12
33E 13
71E-13
34E-12
47E-12
38E-12
93E 13
38E-12
51E-12
1 5E-12
44E-12
2 7E-10
1 6E-10
1 6E-10
1 4E-11
95E-11
70E-13
44E-13
8 1E-11
1 7E-12
53E-14
46E-11
1 1E-11
64E-13
1 6E-09
84E-11
59E-12
44E-09
1 7E-11
60E-13
2 OE-10
35E-11
73E-07
1 1E-07
1 1E-07
95E-11
55E 07
66E-12
75E-07
34E-09
2 2E 13
BSE 13
36E -13
5 2E 13
4 IE 13
76E 13
5 1E 12
45E-13
98E 13
4 7E 12
64E-12
52E-12
1 3E 12
53E 12
70E-12
2 1E-12
6 1E-12
37E-10
22E 10
22E-10
1 BE -08
12E-07
8 7E-10
55E 10
1 OE^)7
21E-09
67E-11
5 BE -08
1 4E^)8
80E 10
20EO6
1 1E-07
69E-11
57E-09
1 4E-08
7 1E-13
47E-12
56E-11
73E-07
8 9E 09
89E-09
1 5E 10
55E-07
1 3E 10
75E-07
34E-09
1 IE 12
24E-11
1 6E-11
4 OE-12
56E 12
46E-11
85E-09
44E-12
2 1E-11
12E-10
63E-11
1 2E-10
2 7E-11
7 8E-11
60E-11
12E-11
7 OE-10
3 OE-10
2 OE-10
55E-09
23E-06
1 4E-06
20E-04
1 1E-10
1 8E-07
21E-04
15E-09
1 1E-08
2 OE-09
1 3E-10
70E-06
16E-07
25E-10
1 3E-09
31E-08
2 1E-14
85E-11
8 1E-10
88E-09
2 7E-07
2 7E-07
3 1E-09
1 3E-06
22E07
5 9E-08
5 OE-09
2 1E-11
35E 10
2 4E-10
6 OE-1 1
85E-11
69E-10
1 3E-07
66E-11
31E-10
1 8E-09
95E-10
1 8E
-------
 TABLE 2  Maximum Modeled Fnvimnmtvilal Fnposure Concentrations
Chemical
2,3,7.8-TCDD
1.2,3,7,6-PeCDD
1,2,3,4,7.8-HxCDD
1,2,3,6.7.8-HxCDD
1,2,3.7,8,9-HxCDD
1,2.3,4,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1,2.3,7,8-PeCDF
2,3,4, 7,8-PeCDF
1,2,3,4,7,8-HxCDF
1, 2,3,8, 7,8-HxCDF
1,2,3,7,8,9-HxCDF
2.3,4.6,7.8-HxCDF
1,2,3,4,6,7,8-HpCDF
1.2.3,4,7.8,9 HpCDF
OCDF
Tetrachtoroblpnenyl
Hexachloroblpnenyt
Heptachtofoblphenyt
Benzo(a)pyrene
Benzo(b)fluoranthene
Bl«(2-«thylhexy1)phthalaie
Carbon tetrachkxfde
Dibenz(a,h)anthracene
Dl(n)ocryl phthslafe
Heptachtor
Hexachlorobenzen*
Hexachlorobutadlene
Hexachtorocyclopentadtene
Hexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
Leafy
Produce
Cone
mg/kgWW
1 5E-12
27E-11
3 7E-11
10E-11
1 2E-11
61E-10
78E-00
22E-11
1 3E-10
1 8E-10
1 2E-10
28E-10
64E-11
20E-10
66E-10
51E-11
1 7E-08
20E-10
35E-10
1 1E-06
1 3E-06
61E-07
69E-04
1 1E-07
1 4E-09
1 3E-04
59E-10
33E-09
32E-09
56E-11
79E-09
1 4E-09
33E-09
1 4E-08
1 1E-07
74E-12
73E-09
1 5E-10
20E-08
1 5E-05
15E-05
24E-09
1 5E-07
2 1E-08 .
53E-09
55E-07
Root
Produce
Cone
mg/kgWW
19E-15
78E-15
38E-15
85E-15
53E-15
35E-14
23E-13
20E-14
48E-14
51E-14
79E-14
74E-14
1 8E-14
84E-14
34E-13
4 2E-14
37E-13
52E-11
82E-12
49E-11
1 1E-11
50E-10
90E-12
40E-08
1 1E-10
95E-09
48E-12
46E-08
1 4E-08
66E-10
26E-08
1 2E-10
1 3E-12
1 3E-12
20E-11
75E-17
61E-12
37E-15
48E-12
1 3E-09
1 3E-09
1 1E-13
28E-11
1 5E-11
92E-15
1 3E-10
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg/kg
20E-12
84E-12
36E-12
59E-12
37E-12
53E-12
50E-13
1 9E-11
55E-11
64E-11
54E-11
5 1E-11
12E-11
58E-11
4 3E-11
53E-12
1 5E-12
1 5E^>8
1 2E-07
8 4E-08
1 6E-07
36E06
58E-08
4 1E-08
1 3E-05
4 1E-07
5 8E-08
39E-04
28E-05
3 2E-08
1 6E-06
16E-05
1 9E-10
1 BE -07
3 4E-08
87E-11
4 7E-07
1 5E-09
90E-07
52E-04
30E-03
3 OE-08
44E-06
34E 10
5 IE 07
22E-06
River
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
1 2E-16
4 9E-16
3 3E-17
1 8E-16
1 1E-16
1 6E-16
30E-15
1 4E-15
2 3E-15
20E-15
1 6E-15
1 5E-15
3 7E-16
1 7E-15
25E-15
31E-16
5 7E-16
28E-12
20E-13
42E-13
27E-12
56E-11
28E-12
1 4E-09
95E-12
65E-12
12E-13
7 2E-10
87E-10
12E-11
31E-10
1 1E-11
1 9E-10
40E-09
85E-09
43E-12
2 1E-10
93E-11
57E-09
1 4E-07
1 4E-07
48E-10
56E 08
69E-10
4 3E-09
5 OE-09
Deer
Cone
mg/kgWW
3 7E-12
6 4E-1 1
4 3E-11
1 1E-V1
1 5E-11
1 3E-10
2 3E-08
1 2E-11
56E-11
32E-10
1 7E-10
3 2E-10
7 4E-11
2 1E-10
1 6E-10
32E-11
1 9E-09
74E-10
4 8E-10
1 5E-08
95E-07
56E-07
79E-O5
34E-11
76E-08
87E-05
6 1E-10
28E09
42E-10
26E-11
31E-06
6 9E-08
35E-10
58E-09
19E-09
27E-12
1 9E-10
33E-10
1 2E-C9
2 8E 08
2 8E-08
24E 09
1 1E 07
4 4E 09
1 2E 07
7 4E 09
Volume V, Appendix/'
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-------
TABLE 2  Maximum Modeled Environmental Exposure Concentrations
Chemical
2.3,7,8TCDD
1, 2,3,7.8- PeCDD
1.2.3.4,7,8 HxCDD
1,2,3,6,7,8-HxCDD
1,2,3,7,8,9-HxCDD
1,2,3.4,6,7,8-HpCDO
OCDD
2,3,7.8-TCDF
1,2,3,7,8-PeCDF
2,3,4, 7,8-PeCDF
1,2,3.4,7,8-HxCDF
1.2,3,6,7,8-HxCDF
1.2,3.7.8,9-HxCDF
2,3,4,6,7,8-HrCDF
1,2,3,4,6,7,8-HpCDF
1,2,3,4,7,8,9-HpCOF
OCDF
Tetrachloroblphenyl
Hexachtoroblphenyf
Heptachloroblphenyl
Benzo(a)pyrene
Benzo(b)fluoranthene
Bi*(2-ethylhexyl)phthala1e
Carbon tetrachtortde
Dlbenz(a,h)anthracene
Dl(n)octyl phthalale
Heptachlor
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
lndeno( 1 ,2 ,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1max
W1 max
W1 max
W1 max
W1 max
W1max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 ma*
W1 max
W1 max
Leafy
Produce
Cone
mg/kgWW
2 1E-11
38E-10
53E-10
1 4E-10
16E-10
86E-09
1 1E-06
31E-10
19E-09
25E-09
1 7E-09
39E-09
90E-10
29E-09
93E-09
72E-10
2 4E-07
28E 09
50E-O9
1 6E-07
1 8E-05
86E-06
9 7E-03
15E-06
19E-08
1 9E-03
82E-09
46E-08
45E-08
78E-10
1 1E-07
19E-08
23E-08
10E-07
7 5E-07
53E-11
50E-08
1 1E 09
1 4E-07
2 1E-04
2 1E-04
1 7E-08
1 OE 06
1 5E-07
39E-08
37E-06
Pool
Produce
Cone
mg/kgWW
2 7E-14
1 IE 13
53E-14
1 2E-13
75E-14
50E-13
32E-12
27E-13
67E-13
72E-13
1 1E-12
1 1E-12
26E-13
1 2E-12
48E-12
60E 13
53E-12
7 3E-10
1 2E-10
68E-10
1 5E-10
70E-09
1 3E-10
56E-07
1 6E-09
1 3E-07
68E-11
64E-07
20E-O7
93E-09
36E-07
1 7E-09
86E-12
84E-12
1 4E-10
50E 16
4 1E-11
25E-14
3 2E-11
1 8E-08
1 8E-08
7 1E-13
1 9E-10
.1 OE-10
62E-14
8 4E-10
River
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
, NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
52E-11
90E 10
6 1E-10
1 5E-10
22E-10
1 BE 09
32E07
1 7E-10
79E-10
45E-09
24E-09
46E-09
10E-09
30E-09
23E-O9
4 5E-10
27E-08
10E-08
68E-09
2 1E-07
1 3E-05
79E-08
1 1E03
4 7E-10
1 1E-06
1 2E-03
86E-09
39E-08
58E-O9
3 7E-10
43E-05
97E-07
25E-09
4 2E-08
13E-08
20E-11
1 4E-09
24E-09
85E-09
39E 07
39E 07
1 7E-08
80E 07
32E-08
8 8E 07
1 7E-08
Volume V, Appendix
-------
TABLE 2  Maximum r/odrlrd Environmental F«poMirr Cnnrrnlfalinns
Chemical
2,3,7,8TCDD
1,2,3.7,8-PeCDO
1, 2,3,4, 7.8-HxCDD
1,2,3,6,7.8-HxCDD
1,2.3,7,8.9-HxCDD
1,2,3,4,6,7,8-HpCDD
OCDD
2,3.7,8-TCDF
1,2,3,7,8-PeCDF
2.3,4.7.8-PeCDF
1,2,3,4,7.8-HxCDF
1 2,3,6, 7.8-HxCDF
1 2,3.7,8.9-H«CDF
2,3,4,6,7,8-HxCDF
1.2.3,4.6.7,8-HpCDF
1,2.3,4,7,8,9-HpCDF
OCDF
Telrachloroblphenyl
Hexachloroblphenyl
Heptachtorobiphenyt
Benzo(a)pyrene
Benzo(b)nuoranthene
Bi»(2-ethylhexyl)phtnalate
Carbon tetrachlorkJe
Olbenz(a.h)anthracene
Dl(n)octy1 phthalate
Heptachk*
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopenladiene
Hexachlorophene
lndeno(1.2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2rrax
W2max
W2max
W2 max
W2max
W2max
W2max
W2 max
W2 max
W2max
W2 max
W2 max
W2max
W2 max
W2 max
1 cm Soil
Cone
mg/kg
1 6E-10
63E-10
53E-10
86E-10
53E-10
61E-09
2BE-08
15E-09
42E-09
4BE-09
8 1E-O9
76E-09
1 9E-09
87E-09
50E-08
6 1E-09
87E^)8
20E-07
32E-07
32E-07
34E-06
19E-05
1 1E-06
1 1E-05
4 7E-06
48E-07
95E-09
18E-05
50E-05
81E-07
1 3E-05
53E-06
87E-07
34E-05
41E-05
89E-08
49E-07
23E-06
15E-04
93E-04
93E-04
34E-06
63E-04
3 1E-06
1 6E-O4
22E^5
Beef
Cone
mg/kgWW
92E 11
1 6E-09
1 OE-09
26E-10
37E-10
31E09
5 6E-07
29E-10
1 4E-09
78E-09
42E-09
79E-09
1 8E-09
51E-09
4 OE-09
7 7E-10
4 6E-08
2 OE 08
1 3E 08
36E-07
30E05
1 8E-05
25E-03
1 3E 09
1 9E-06
27E-03
1 9E-08
1 4E-07
25E-08
1 6E-09
76E-05
1 8E-06
8 OE-09
14E-07
43E-08
75E-11
44E-09
95E-09
3 3E-08
85E-07
85E-07
5 8E-08
28E-06
1 OE-07
37E-06
6 1E-08
Pork
Cone
mg/kgWW
22E-11
29E-10
1 9E-10
57E-11
73E-11
53E-10
94E-08
64E-11
26E-10
1 5E-09
87E-10
1 5E-09
34E-10
1 OE-09
85E-10
1 8E-10
79E-09
1 6E-08
96E-09
69E-08
19E-06
1 4E-06
1 6E-04
50E-10
2 2E-07
1 8E-04
14E-09
1 3E-07
2 9E-08
1 7E-09
46E-06
2 2E-07
32E-09
4 6E-08
1 9E-07
62E-11
1 9E-10
1 2E-08
9 3E-08
28E-06
2 8E-06
25E-07
6 8E-05
22E-09
1 5E-05
1 6E 08
Chicken
Cone
mg/kgWW
7 7E-13
29E 12
1 2E-12
1 7E-12
1 3E 12
, 24E 12
1 6E 11
16E 12
34E-12
1 6E-11
2 1E-11
1 7E-11
43E-12
1 7E 11
22E-11
67E-12
1 9E-11
1 3E 09
79E 10
8 1E-10
67E-11
47E-10
33E 12
22E 12
35E-10
84E-12
2 7E-13
23E-10
55E-11
32E-12
68E-09
36E-10
23E-11
1 7E-08
69E-11
24E-12
78E 10
1 4E-10
29E 06
53E 07
53E-07
38E-10
22E 06
26E-11
30E 06
1 3E 08
Egg
Cone
mg/kgWW
1 1E 12
40E 12
1 6E-12
2 3E-12
' 1 BE 12
33E-12
22E 11
22E 12
48E-12
23E-11
29E-11
23E-11
59E 12
24E-11
3 1E-11
92E-12
26E-11
1 8E-09
1 1E 09
1 IE 09
8 5E-08
59E-07
4 1E-O9
27E-09
4 4E-07
1 OE-08
33E-10
2 9E-07
69E-08
4 OE-09
85E-06
4 6E-07
2 7E-10
2 3E-08
5 5E-08
28E-12
1 8E-11
22E-10
29E-06
4 4E-08
4 4E-08
6 1E-10
2 2E-06
52E-10
30E06
1 3E 08
Milk
Cone
mg/kgWW
69E-12
1 2E 10
79E-11
20E-11
28E 11
23E-10
4 2E 08
22E 11
1 OE 10
59E-10
3 1E-10
59E-10
1 4E-10
39E 10
30E 10
58E-11
35E 09
1 5E 09
99E-10
2 7E-08
1 2E-05
69E-06
9 8E-04
55E-10
76E-07
1 1E-03
76E-09
56E-O8
1 OE-08
63E-10
30E-05
7 OE-07
1 OE-09
53E-09
1 2E-07
85E-14
34E-10
32E-09
35E 08
1 4E 06
1 4E-06
1 2E-08
53E06
86E 07
23E 07
2 OE-08
Cheese
Cone
mg/kgWW
1 OE-10
1 8E-09
1 2E 09
29E-10
42E-10
35E 09
6 3E-07
33E-10
1 5E-O9
8BE-09
47E-09
89E-09
2 OE-09
58E-09
45E-09
87E-10
52E-08
23E-08
1 5E-08
41E^)7
12E-05
69E-06
98E-O4
55E-10
76E-O7
1 1E-03
76E-09
56E-O8
1 OE-08
83E-10
30E-05
7 OE-07
1 OE-09
53E-09
12E-07
85E-14
34E-10
32E-09
3 5E-08
14E-06
1 4E-06
1 2E-08
53E06
8 6E-07
2 3E-07
2 OE-08
Milk
Dessert
Cone
mg/kgWW
45E 11
76E-10
5 1E-10
1 3E-10
1 8E-10
1 5E-09
2 7E-07
1 4E-10
67E-10
38E-09
2 OE-09
39E-09
B8E 10
25E-09
1 9E-09
38E-10
2 3E-08
98E-09
64E-09
1 8E-07
12E-05
69E-O6
98E-04
55E-10
76E-07
1 1E-03
76E-09
56E-08
1 OE-08
63E-10
30E-05
7 OE-07
1 OE-09
53E-09
1 2E-07
85E-14
34E-10
32E09
3 5E-08
1 4E 06
1 4E-06
1 2E 08
53E-06
86E 07
23E 07
2 OE 08
Yogurt
Cone
mg/kgWW
69E 12
1 2E-10
79E 11
20E 11
28E-11
23E 10
4 2E 08
22E-11
1 OE 10
59E-10
31E 10
59E-10
1 4E 10
39E-10
3 OE-10
58E 11
35E-O9
1 5E-C9
99E-10
2 7E-08
1 2E-05
69E-06
9 8E-04
55E-10
76E-07
1 1E-03
76E-09
56E^)8
1 OE-08
63E-10
30E-05
70E^)7
1 OE-09
53E-09
12E^)7
85E-14
34E-10
32E-03
35E4)8
1 4E 06
1 4E 06
1 2E 08
5 3E 06
86E 07
2 3E 07
20E 08
Cream
Cone
mg/kgWW
86E-11
1 5E 09
99E-10
25E-10
35E-10
29E-09
53E 07
27E-10
1 3E-09
74E-09
39E-09
74E-09
1 7E-09
4 8E-09
37E09
72E-10
44E08
1 9E-08
1 2E-08
3 4E-07
1 2E-05
69E-06
9 8E-04
55E-10
76E-07
1 1E 03
76E4»
5 6E-08
1 OE-08
63E-10
30E-05
7 OE-07
1 OE-09
53E-09
1 2E-07
85E-14
34E-10
32E-09
35E 08
1 4E 06
1 4E 06
1 2E 08
5 3E-06
86E 07
2 3E 07
? OF OB
Butter
Cone
mg/kgWW
28E-10
4 BE -09
32E-09
8 1E-10
1 1E-09
94E-09
1 7E-06
9 OE-10
42E-09
2 4E 08
1 3E-08
2 4E-08
55E-09
1 6E-08
1 2E 08
24E-09
1 4E-07
6 2E 08
4 OE-08
1 1E-06
1 2E-05
69E-06
9BE-O4
55E-10
7 6E-07
1 1E-03
76E-09
56E-O8
1 OE-08
63E-10
30E-05
7 OE-07
1 OE-09
53E09
1 2E-07
85E-14
34E-10
32E09
3 5E 08
1 4E 06
1 4E 06
1 2E 08
53E 06
86E 07
2 3E 07
2 OF 08
E»posed
Produce
Cone
mg/kgWW
1 4E-13
25E-12
34E-12
1 OE-12
1 1E-12
56E-11
7 1E 09
21E 12
1 2E 11
1 7E-11
1 2E-11
26E-11
60E 12
19E-11
66E-11
55E-12
1 5E-09
38E 11
3BE-11
1 OE-09
1 2E^)7
56E-08
62E-05
9 7E 07
42E 09
1 2E^)5
53E-11
58E-09
25E08
1 6E-10
2 3E 08
42E-09
46E 09
25E08
1 2E 07
1 6E 11
1 6E 08
46E 10
3 BE 08
24E 05
2
-------
 TABLE 2  Maximum Modeled Environmental Exposure Concrntratio
Chemical
2,3,7.8-TCDD
1.2.3.7,8-PeCDD
1.2,3.4.7,e-HxCDD
1.2.3,6.7,8-H)(CDD
1.2,3.7,8,9-HxCOD
1, 2,3,4,6, 7,8-HpCDD
OCDD
2,3,7,8-TCDF
1.2,3.7,8-PeCDF
2.3.4, 7,8-PeCDF
1,2.3.4,7,8-HxCDF
1, 2.3.8, 7,8-HKCDF
1.2,3,7.8,9-HxCDF
2,3,4,6,7,8-HirCDF
1.2.3,4,6.7,8-HpCDF
1,2.3,4,7,8,9-HpCDF
OCDF
T etrachlor oblpbenyl
Hexachloroblphenyl
Heptachloroblphenyl
Benzo(a)pyrene
Benzo(b)fluor»nthene
Bi«(2-ethylhexy1)phthalate
Carbon letrachloride
Dlbenz(a,h)anthracene
D)(n)octy1 phthalate
Heptachtor
Hexachtorobenzene
Hexachlorobutadiene
Hexachtoroeyclopentadlene
HexachkKophene
Indenof 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (heravalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2mw
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2 max
Leafy
Produce
Cone
mg/kgWW
75E-12
1 4E-10
1 9E-10
51E-11
58E-11
3 1E-09
39E-07
t 1E-10
6 7E-10
9 1E-10
6 1E-10
1 4E-09
32E-10
1 OE-O9
33E-O9
25E-10
84E-O8
9BE-10
1 8E-09
5 7E-08
63E-06
31E-06
35E-03
54E-07
59E-09
66E-04
29E-09
1 7E-08
16E-08
2 8E-10
34E-08
59E-09
1 3E-08
58E-08
4 3E-07
29E-11
29E-08
59E-10
80E-08
76E-05
76E-05
96E-09
5 9E-07
85E-08
2 IE-OS
22E-OG
Root
Produce
Cone
mg/kgWW
94E-15
37E-14
1 7E-14
38E-14
23E-14
1 5E-13
99E-13
96E-14
23E-13
24E-13
35E-13
33E-13
84E-14
38F 13
1 5E-12
1 9E-13
1 6E-12
2 6E-10
4 1E-11
2 4E-10
51E-11
25E-09
4 2E-11
2 OE-07
4 7E-10
48E-08
24E-11
23E-O7
69E-08
33EO9
1 1E-07
52E-10
50E-12
49E-12
81E-11
30E-16
24E-11
1 5E-14
19E-11
65E-09
65E-09
42E-13
1 1E-10
60E-11
37E-14
50E-10
River
Fish
Cone
mg/kg
1 6E 11
70E 11
1 1E-10
1 3E-10
83E-11
1 9E-10
14E-11
1 2E-10
56E-10
80E-10
1 2E-09
1 1E-09
26E-10
12E-09
1 4E-09
1 7E-10
59E-11
1 1E 08
9 7E-07
3 BE 07
1 5E 06
77E06
92E-07
1 8E-08
76E-05
2 OE-07
3 1E-08
1 8E-04
12E-05
1 4E-08
1 2E-06
96E-05
97E-11
9 3E-08
1 7E-08
50E-11
2 OE-07
88E-10
5 4E-07
2 3E 04
1 3E-03
1 6E 08
24E 06
1 7E-10
33E 07
1 1E-06
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA
• NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
92E 16
4 1E-15
10E-15
39E-15
2'jE-15
55E-15
85E-14
90E-15
23E-14
25E-14
35E-14
33E-14
78E-15
37E-14
80E-14
10E-14
22E-14
20E-12
t 6E-12
1 9E-12
27E-11
1 2E-10
45E-11
59E-10
57E-11
32E-12
62E-14
34E-10
39E-10
55E-12
25E-10
62E-11
97E-11
21E-09
43E-09
25E-12
92E-11
55E-11
33E-09
6 OE-08
6 OE 08
26E-10
3 1E-08
35E 10
2 7E 09
25E 09
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
1 9E 11
32E-10
22E-10
53E-11
76E-11
63E-10
1 2E-07
59E-11
28E-10
1 6E-09
85E-10
1 6E-09
37E-10
1 1E-09
8 1E-10
16E-10
95E-09
37E-O9
24E-09
74E-08
47E-06
2BE-06
40E-04
1 7E-10
33E-07
44E-O4
31E-09
14E-08
21E-09
1 3E-10
13E-05
3 OE-07
14E-09
2 3E-08
74E-09
1 1E-11
7 7E-10
13E-09
4 7E-09
1 4E-07
1 4E-07
95E-09
4 4E 07
1 BE -08
4 9E 07
97E-09
Volume V, Appendix V-11
                                                                                            14-
n
-------
  TABLE 2  Maximb.    ,,ieled Environmental Exposure Concrnlralions
Chemical
2,3.7,8-TCDD
1.2,3,7.8-PeCDD
1,2,3.4, 7.8-HxCDD
1,2,3,6,7.8 HxCDD
1,2,3,7.8,9-HxCDD
1, 2,3,4,6, 7,8-HpC DO
OCDD
2.3,7,8-TCDF
1,2.3,7,8-PeCDF
2,3,4,7,8-PeCDF
1, 2,3,4, 7.8-HxCDF
1,2,3,6,7,8-HxCDF
1,2,3,7,8.9-HxCDF
2,3,4,6,7.8-HxCDF
1,2.3,4,6,7,8-HpCDF
1,2,3,4,7.8,9 HpCDF
OCDF
Tetrachloroblphenyt
Hexachloroblphenyl
Heptachforoblphenyl
Benzo(a)pyrene
Benzo(b)fluor«nthene
Bis(2-ethy1hexyl)ph(halale
Carbon Mrachtoride
Oibenz(a,h)anthracene
Dt(n)octy1 phthalate
Heptachlcx
Hexachlorobenzene
Hexachlorobutadlene
Hexachlorocyclopentadlene
Hexachlorophene
Indenof 1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
W3ma«
W3max
W3max
W3 max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3 max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
VV3max
W3max
W3max
W3max
1 cm Soil
Cone
mg/kg
50E-11
1 8E-10
1 4E-10
2 1E-10
1 3E-10
15E-09
66E-09
49E-10
13E-09
14E-09
21E-09
20E-09
R 5F.m
22E-09
12E-08
15E-09
20E-08
63E 08
1 1E-07
10E-07
10E-06
62E-06
3 1E-07
36E-06
1 1E-O6
16E-07
31E-09
59E-06
16E-05
26E-07
30E-06
12E-06
21E-07
80E-06
99E-06
21E-08
1 2E-07
56E-07
35E-05
30E-04
3 OE 04
8 2E-07
1 5E-04
7 4E 07
37E-05
53E-06
Beef
Cone
mg/KgWW
30E-11
50E-10
34E-10
8 IP 1 1
12E-10
99E-10
18E-07
94E-11
44E-10
25E-09
13E-09
25E-09
1 7E-09
1 3E-09
24E-10
1 5E 08
64E-09
42E^)9
1 2E-07
96E 06
57E-06
81E-04
4 1E-10
4 7E-07
6 9E-04
63E-09
4 5E-08
82E-09
51E-10
18E-05
43E-07
20E-09
3 5E-08
1 1 E-08
1 8E-11
1 1E-09
23E-09
82E09
2 7E-07
2 7E-07
1 4E 08
69E-07
2 5E-08
91E-07
1 5E-08
Pork
Cone
mg/kgWW
72E-12
92E-11
59E-11
23E-11
1 7E-10
3 OE-08 '
2 1E-11
83E-11
4 7E-10
27E-10
46E-10
1 IE-ID
31E-10
26E-10
54E-11
26E-09
50E-09
3 1E-09
22E-08
63E-07
45E-07
52E-05
1 6E-10
5 OE-08
57E-05
45E-10
41E-08
93E-09
56E-10
1 1E-06
52E-08
78E-10
1 1E-08
45E-08
1 5E-11
4 7E-11
29E-09
22E-08
9 1E-07
9 1E-07
59E-08
1 6E-05
53E-10
36E-06
3 7E-09
Chicken
Cone
mg/kgVWV
24E 13
BSE 13
3 IE 13
4 1E-13
32E 13
59E 13
3 BE 12
52E-13
1 1E 12
49E 12
53E 12
43E 12
1 1E-12
44E 12
56E-12
1 6E 12
45E-12
43E 10
26E 10
26E-10
20E-11
1 5E-10
94E-13
7 1E 13
82E 11
27E 12
86E 14
75E-11
18E-11
1 OE-12
1 6E 09
85E-11
56E-12
42E-09
1 7E-11
57E-13
1 9E 10
33E 11
69E 07
1 7E 07
1 7E-07
90E-11
52E-07
62E 12
7 1E-07
32E-09
Egg
Cone
mg/kgWW
33E-13
1 2E-1?
4 3E-13
5 7E-13
44E-13
8 1E-13
52E-12
71E-13
1 4E-12
67E-12
74E-12
60E-12
1 6E-12
61E-12
7BE-12
22E-12
62E-12
59E-10
35E-10
36E-10
25E-08
19E-07
12E^)9
89E-10
1 OE-07
34E-09
1 1E-10
9 4E-08
2 2E-08
1 3E-09
20E-06
1 1E-07
65E-11
54E-09
1 3E-O8
67E-13
44E-12
53E-11
69E-07
1 4E-08
1 4E-08
15E-10
52E-07
1 2E 10
7 1E 07
3 2E-09
Milk
Cone
mg/kgWW
22E 12
3BE 11
26E 11
63E-12
90E 12
74E-11
1 4E-08
7 1E-12
33E-11
1 9E-10
1 OE-10
1 9E-10
44E-11
1 2E-10
95E-11
18E-11
1 1E-09
49E 10
32E-10
89E-O9
38E-06
22E-06
32E-04
1 8E-10
1 8E-07
35E-O4
25E-09
18E-08
33E4)9
2 OE-10
73E-06
1 7E-07
25E-10
1 3E-09
3 IE-OS
21E-14
85E-11
79E 10
86E-09
4 4E-07
44E07
30E09
1 3E-06
2 1E-07
57E 08
48E-09
Cheese
Cone
mg/kgWW
33E-11
5 7E-10
38E-10
94E-11
1 3E-10
1 1E-09
21E-07
1 1E-10
5 OE-10
29E-09
15E-09
29E-09
65E-10
19E-09
14E-09
27E-10
1 7E-08
73E-09
48E-09
13E-07
38E-06
22E-08
32E-04
1 8E-10
18E-07
35E-04
25E-09
18E-08
33E-09
2 OE-10
73E-06
1 7E-07
25E-10
1 3E-09
31 E-08
2 1E-14
85E-11
79E-10
86E-09
4 4E-07
44E-07
30E-09
1 3E-06
2 1E-07
5 7E-08
48E-09
Milk
Dessert
Cone
mg/kgWW
1 4E-11
25E-10
1 7E-10
4 IE 11
58E-11
48E-10
8 9E-08
46E-11
22E-10
12E-09
65E-10
1 2E-09
28E-10
8 1E-10
62E-10
1 2E-10
74E-O9
32E-09
21E-09
5BE-08
38E-06
22E-06
32E-04
1 8E-10
18E-07
3 5E-04
25E-09
18E-08
33E-09
2 OE-10
73E-06
1 7E-07
25E-10
1 3E-09
3 1E-08
21E-14
85E-11
79E-10
86E-09
44E-O7
44E-07
30E 09
1 3E-06
2 1E 07
5 7E 08
4 BE -09
Yogurt
Cone
mg/kgWW
2 2E-12
38E-11
26E-11
63E-12
9 OE-12
74E-11
1 4E-08
71E-12
33E-11
1 9E-10
1 OE-10
1 9E-10
44E-11
1 2E-10
95E-11
1 8E-11
1 1E-09
49E-10
32E-10
89E-09
38E-06
22E-06
3 2E-04
18E-10
1 8E-07
35E-04
25E-09
1 8E-08
33E-09
2 OE-10
73E-O6
1 7E-07
25E-10
1 3E-09
3 1E-08
2 1E-14
85E-11
79E-10
8 8E-09
44E 07
44E 07
30E-09
1 3E 06
2 IE 07
5 7E 08
4 BE 09
Cteam
Cone
mgftgWW
2BE-11
48E-10
32E 10
78E-11
1 tE-10
93E-10
1 7E-07
89E-11
4 2E-10
24E-09
1 3E-09
24E-09
5 5E-10
16E-09
12E-09
2 3E-10
1 4E-08
61E-09
40E-09
1 1E-07
38E-06
22E-06
32E-04
1 8E-10
18E-07
35E^)4
25E-09
1 8E-O8
33E-09
2 OE-10
73E-06
1 7E-07
2 5E-10
1 3E-09
31E-08
2 1E-14
85E-11
79E-10
86E-O9
4 4E 07
4 4E 07
30E 09
1 3E 06
2 1E 07
5 7E 08
4 BE 09
Butler
Cone
mg/kgWW
9 1E-11
16E-09
1 OE-09
26E-10
3 7E-10
31E-09
56E-07
2 9E-10
1 4E-O9
78E-09
41E-09
78E-09
18E-09
5 1E-09
39E-09
75E-10
46E-08
2 OE-08
13E-08
36E-07
38E-06
22E-06
32E-04
1 8E-10
18E^)7
35E-04
25E-09
1 BE -OB
33E-09
2 OE-10
73E-06
1 7E-07
25E-10
13E-09
31E4W
21E-14
85E-11
79E-10
86E09
44E 07
44E 07
30E 09
1 3E 06
2 1E 07
5 7E OB
4 BE OT
Exposed
Produce
Cone
mg/kgWW
46E-14
BOE-13
1 1E-12
33E 13
36E-13
1 8E-11
23E-09
67E-13
4 OE-12
54E-12
38E-12
B4E-12
19E-12
62E-12
2 1E-11
1 7E-12
49E-10
1 2E-11
12E-11
33E-10
38E-08
18E08
20E05
3 1E-07
10E09
39E-06
1 7E-11
1 9E-09
8 OE-09
53E-11
57E^)9
1 OE 09
1 1E 09
61E09
30E 08
4 1E 12
39E 09
1 IE 10
9 IE 09
7 7E 06
7 7E 06
33E 09
1 BE 07
9 7E 09
3 BE 09
55E 07
Protected
Produce
Cone
mg/kgWW
33E-15
1 2E 14
2 OE-15
58E-15
1 8E-15
1 2E-14
1 2E-13
38E-14
70E-1*
64E-14
56E-14
53E 14
1 4E-14
8 1E-14
1 5E-13
1 BE-14
75E-14
1 1E-11
34E-12
1 7E-12
1 3E-10
71E-10
80E 12
55E07
65E-11
1 5E-12
32E-13
32E4)9
1 4E 08
9 1E-11
60E-11
78E 11
12E4H
39E^»
26E-08
1 OE-12
39E 09
67E 11
8 IE 09
1 3E 05
1 3E 05
50E 09
22E 07
1 4E 08
29E 10
9 5E 07
Volume V, Appendix V-11
-------
 TABLE 2  Maximum Modeled Environmental Exposure Concentrations
Chemical
2,3.7.8 TCDD
1. 2.3,7. 8-PeCDO
1,2,3,4. 7,8-HxCDD
1,2,3.8.7,8 HxCDD
1,2,3,7,8,9-HxCDD
1, 2,3,4 ,6,7,8-HpCDD
OCDD
2,3,7,8-TCDF
1.2,3,7.8-PeCDF
2,3,4. 7,e-P«CDF
1,2,3,4,7,8-HxCDF
1,2,3,6,7,8-HxCDF
1.2,3,7,8.9-HxCDF
2,3.4,6,7,8-HxCDF
1.2,3.4.6,7,8-HpCDF
1,2.3,4, 7,8.9-HpCDF
OCDF
Telrachlorobiphenyl
Hexachtorobiphenyl
Heptachkjroblpnenyl
Benzo(a)pyren«
Benzo(b)fluoranthene
Bla(2~ethylhexyl)phthalate
Carbon tetrachloride
Dlbenz(a,h)anthracene
Di(n)octy1 phthalate
Heptachtor
Hexachlorobenzene
Hexachkxobutadlene
Hexachlorocyclopentadlene
Mexachlorophene
lndeno(1 ,2,3-cd)pyrene
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Lead
Mercury
Mercury (methyl BCF)
Nickel
Selenium
Silver
Thallium
Zinc
Subarea
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3m«
W3m»x
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3 max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
Leaty
Produce
Cone
mg/kgWW
24E-12
44E-11
6 1E-11
16E-11
1 9E-11
9 9E-10
1 3E-07
36E-11
2 2E-10
2 9E-10
2 OE-10
4 5E-10
1 OE-10
33E-10
1 1E-09
82E-11
27E-08
32E-10
57E-10
1 8E-08
2 tE-06
99E-07
1 1E-03
1 7E-07
1 4E-09
21E-04
95E-10
54E-09
52E-09
90E-11
82E-09
1 4E-09
32E-09
1 4E-08
1 OE-07
7 2E-12
70E-09
1 4E-10
19E-08
24E-05
24E-05
23E-09
1 4E-07
20E-08 .
53E-09
5 2E-07
Root
Produce
Cone
mg/kgWW
29E-15
1 1E-14
44E-15
94E-15
56E-15
36E-14
23E-13
31E-14
70E-14
7 2E-14
90E-14
8 5E-14
23E-14
9 BE 14
38E-13
45E-14
38E-13
84E-11
1 3E-11
79E-11
1 5E-11
8 OE-10
1 2E-11
85E-08
1 1E-10
1 5E-08
78E-12
74E-O8
22E-08
1 1E-09
26E-08
1 2E-10
1 2E-12
12E-12
19E-11
7 1E-17
58E-12
35E-15
45E-12
2 1E-09
21E-09
99E-14
2 7E-11
1 4E-11
87E-15
1 2E-10
River
Fish
Cone
mg/kg
1 6E-11
72E-11
1 1E-10
1 3E-10
84E-11
1 9E-10
15E-11
1 2E-10
5 7E-10
82E-10
1 2E-09
1 1E-O9
2 7E-10
1 3E 09
1 4E-09
1 8E-10
60E-11
1 1E-08
1 OE-06
39E-07
16E-06
8 OE-06
96E-07
1 BE -08
7 BE 05
2 1E-07
32E-08
1 9E-04
1 3E-05
1 5E-08
1 3E-06
99E-05
99E-11
95E-08
1 BE -08
50E-11
2 1E-07
89E-10
54E-07
2 3E-04
1 3E 03
1 6E-08
24E-06
18E-10
3 3E-07
1 1E-06
Lake
Fish
Cone
mg/kg
NA
NA
NA
NA
NA
NA.
tin
' NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
River
Water
Cone
mg/L
94E-16
4 2E 15
1 OE-15
40E-15
25E-15
c cr 4c
J DC- ID
87E-14
93E-15
24E-14
26E-14
36E-14
3-»c 44
JC- 1*1
BOE-15
38E-14
81E-14
10E-14
22E-14
21E-12
1 7E-12
20E-12
28E-11
1 3E-10
47E-11
61E-10
58E-11
33E-12
64E-14
35E-10
41E-10
57E-12
25E-10
64E-11
99E-11
22E-09
44E-09
25E-12
94E-11
56E-11
34E-09
6 2E-08
6 2E-08
26E-10
31E-08
35E 10
2 BE 09
26E-09
Lake
Water
Cone
mg/L
NA
NA
NA
NA
NA
U A
Ftr\
NA
NA
NA
NA
NA
MA
rin
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Deer
Cone
mg/kgWW
6 OE-12
1 OE-10
7 OE-11
1 7E-1,1
24E-T1
<^ nc 4n
2 Ut-10
3 7E-08
1 9E-11
9 OE-1 1
52E-10
2 7E-10
(? TC 4 A
j 2E-11I
1 2E-10
34E-10
26E-10
5 OE-11
3 1E-09
1 2E-O9
7 8E-10
24E-08
15E-06
91E-07
1 3E-04
55E-11
79E-08
1 4E-04
9 9E-10
45E-09
6 7E-10
43E-11
32E-06
73E-08
35E-10
57E-09
1 8E-09
27E-12
1 9E-10
33E-10
1 2E-09
45E-08
45E-08
2 3E-09
1 1E 07
43E-09
1 2E-07
24E-09
Volume V, Appendlr    \
-------
                            APPENDIX V-12

           Estimation of Average Cancer and Noncancer Exposure Dose
             (LADD and ADD) for Subsistence Fanner in Subarea El
Volume V
A.r>r»endiY
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        Avg Cjntni .»ri(l Norn
                               E»pns i JIM OOSH Adull
                                                            F .11 mm
                                      LIFETIME AVERAGE DAILY DOSE (LADD) FOR CHEMICALS WITH CARCINOGENIC HEALTH EFFECTS
Chemical
2 3 78 TCDD
1 2.3.? 8 PeCDO
12 34 78H«COD
1.2 36 78 HuCDD
1.2 3.7.89H.CDO
1.2,3.4.6.7.8-HpCOD
OCOO
2.3.7.8 TCDF
1.2.3.7 8 PeCDF
2.3.4.7.8 PeCDF
2,34 7BH«COF
.2.3.6.7.8H»CDF
2.3.789H«CDF
3.46 7BH«CDF
2 3.4.6 7.8 HpCDF
2 3.4.7.8.9 HpCOF
OCDf
T alt achloiobiphenyl
Henaehloiobiphenyt
Meplachtoiobiphenyl
Ban;o(a)pyi0no
B«nio(b)fl«KManlhene
Bls(2-elhvlhe»y)polhalalfl
Carbon latrachkxKto
Dibeni (a ,h)anlhi acene
Di(n)octy1 phlhalale
Heptachtoi
Hexachkxoban/ene
Hexachlofobuladiene
Hevachloiocyclopenladiene
He*achto«ophene
Indeno) 1 .2.3 cd)pyiene
Antimony
Ai sonic
Banum
Beryllium
Cadmium
Chlomium (heiavatenl)
Lead
Mmcury
Nickel
Selenium
Silvei
Ttullium
7i.ir
Subaiea
El avg
El avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
Etavg
El avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
Etavg
Et avg
Et avg
El avg
El avg
El avg
Et avg
Etavg
El avg
El vg
El vg
Et vg
El vg
El vg
El vg
E1 avg
Piolecled
Pioduce
tngeslion
mg/kg d
22E 18
1 IE 17
26E 18
906-18
30C 18
206-17
22E-16
236-17
536 17
55E 17
796-17
74E 17
1 76 17
84E 17
2 3E 18
29E 17
1 3E 16
64E 15
t 9E 15
9 3E 16
t IE 13
40E 13
78E IS
30E 10
1 2E 13
82E 16
1 8E 16
1 7E 12
7 BE 12
5 OF, 14
1 IE 13
1 4E 13
2 IE 12
706 12
466 11
1 8E IS
70E 12
126 13
1 4E It
7 4E 09
8 BE 12
40E 10
25E 11
5 2E 13
1 7E-O9
Lealy
Pioduce
Ingeshon
mg/kg d
1 IE-IS
206 14
27E 14
7 4E IS
85E 15
45E 13
57E-11
1 6E 14
986-14
1 3E 13
906 14
2 IE 13
4 7E 14
1 5E 13
48E 13
3 7E 14
1 2E 11
1 4E 13
26E 13
8 3E 12
92E 10
4 5E 10
5 IE 07
79E 11
20E 12
2 4E 09
4 3E 13
2 4E 12
2 3E 12
4 IE 14
1 2E-H
20E 12
45E 12
206 11
1 56 10
99E 15
99E 12
20E 13
2 7E 11
1 1E 08
33E 12
20E 10
29E It
7 IE 12
75E 10
Root
Pioduce
Ingnslion
mg/kg-d
4 7E 18
23E 17
1 4E 17
34E 17
22E 17
1 SE 16
9 BE 16
45E-17
1 3E 16
1 4E 16
306 16
2 BE 16
85E 17
32E 16
t 3E 15
1 7E 16
1 6E 15
1 IE 13
1 7E 14
1 OE 13
30E 14
1 1E 12
28E 14
BSE 11
4 7E 13
20E It
1 OE 14
9 7E 11
29E 11
1 4E 12
1 IE 10
52E 13
5 IE 15
SOE IS
6 IE 14
30E 19
24E 14
15E 17
19E 14
2 7E 12
42E 16
1 IE 13
SOE 14
3 7E 17
SOE 13
Enposed
Fiuil
Ingflshon
rng/kg d
4 7E 17
BOE 16
1 IE 15
3 BE 16
39E 16
't BE 14
22E-12
6 BE 16
39E 15
53E 15
42E 15
86E 15
20E 15
66E 15
2 4E 14
2 IE 15
4 BE 13
1 2E 14
t 2E 14
32E 13
3 BE 11
1 BE 11
20EOB
30E 10
30E 12
92E 11
t /E 14
1 BE 12
7 BE 12
5 IE 14
I If 11
30E 12
34E 12
1BE 11
9 IE-It
1 2E 14
1 2E 11
33E 13
2 7E 11
7 4Efl9
1 OE 11
54E 10
30E 11
1 1E 11
1 7E 09
Piolecled
Fruit
Ingeslion
mg/kg d
53E IB
26E 17
63E 18
2 IE 17
72E 18
48E 17
52E 16
56E 17
1 3E 16
t 3E 16
1 9E 16
18E 16
4 1E 17
20E 16
S5E 16
70E 17
32E 16
1 5E 14
45E 15
22E 15
25E 13
95E 13
t 9E 14
73E 10
2 BE 13
20E 15
42E 16
42E 12
19E 11
1 2E 13
26E 13
34E 13
5 IE 12
1 7E 11
1 IE 10
43E 15
1 7E 11
2 BE 13
35E 11
1 BE 08
2 IE tl
95E 10
6 1E 11
1 2E 12
40E 09
Rivei
Walei
Ingestmn
ing/kg d
33E 22
1 6E 21
42E 22
t 7E 21
1 1E 21
24E-21
3 BE 20
32E 21
86E 21
95E 21
1 SE 20
1 4E 20
32E 21
1 6E 20
34E 20
44E 21
9SE 21
68E 19
S5E 19
6SE 19
1 IE 17
4 IE 17
2 IE 17
20E 16
t 7E 17
1 IE 18
2 IE 20
1 IE 16
1 3E 16
19E 18
1 1E 16
19E 17
43E 17
9SE 16
19E 15
1 1E IB
42E 17
24E 17
15E 15
20E 14
IE 16
4E 14
6E 16
2E 15
1F IS
Rivei
Walei
Doimal
Contact
nig/hg d
1 4E 18
54E 18
74E 18
1 3E 17
19E 17
64E 17
29E 16
1 3E 17
42E 17
57E 17
1 36 16
t 2E 16
2 BE 17
t 4E 16
62E 16
806 17
596 16
1 BE tS
43E 15
94E 15
32E 14
14E 13
1 6E 13
4 7E 15
1 IE 13
306 14
34E 17
196 13
446 14
1 56 15
1 IE 12
1 IE 13
1 66 17
34E 16
7 IE 16
406 19
1 SE 17
89E 18
54E 16
74E 15
4 1E 17
49E 15
56E 17
44E 16
4 IE 16
Lake
Walei
Ingostton
mg/kg d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
Lake
Walei
Deicn.il
Contact
mg/kg -d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Infant
Biaasl milk
Ingeshon
mg/kg d
46E 14
75E 13
52E 13
1 46-13
196 13
1 7E 12
306 10
1 56-13
7 IE 13
386 12
226 12
39E 12
906 13
26E 12
246 12
466 13
296 It
1 26 It
786 12
1 8E 10
86E 08
62E 08
1 36 06
23E 12
SOE 08
166 03
7 BE 11
606 10
22E 11
28F 12
1 3E OS
436 08
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
NA
Vulttmn V A|i}x>n
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                            APPENDIX V-13

          Estimation of Maximum Cancer and Noncancer Exposure Dose
             (LADD and ADD) for Subsistence Farmer in Subarea El
Volume V
Appendix V-13
-------
           M.n Crfiu IM .mil Nimi .IMI in E iprisuic DMSP Ailull nuliMsli-iii p F,1111101
                                            1 IFE TIME AVERAGF OAll V DOSE (LADD) FOR CHEMICALS WITH CARCINOGENIC HEALTH EFFECTS
           Chemical
 2.3 7.8 TCDD
 1.2 3,7.8 PeCDD
 1.2.3,4.7.SH«CDD
 1.2.3 6.7.8 HiCOO
 1.2,3 78.9 H«CDD
 1.2.3,4.6.7.8 HpCDO
 OCDD
 2.3.7.8 TCDF
 1.2.3.78 PeCDF
 2.3.4,7.8 PeCDF
 1.2.3.4,7.8 HKCDF
 1.2.3.6.7 8 H»CDF
 1 2.3 7 8.9 H«CDF
 2346 7.8 H»CDF
 1.2.3.4.6 78 HpCDF
 1.2.3,4.7.8.9 HpCDF
 OCDF
 T ell achlni nbiphenyl
 Heiachloinbiplianyt
 Haplachkiiobiphenyt
 Ban/o(a)pyrena
 Ban2o(b)(luoianlhena
 Bis(2 •alhytham/1)phlhalale
Carbon leliachloitde
 Oiban;(a .h)anlhr acnne
 Di(n)oclyl phlhalala
 Haptachloi
 Havachfoioban/ana
 MaKachlwobuladiane
 Hanachlaiocyclopenladiene
 Hanacnlniophane
 lndeno(1.2.3-cd)pyiana
Anlimony
 Aisanic
 Barium
 Baiytlmm
Cadmrum
Chromium  (hanavalanl)
load
Mercury
 NK kel
 Sflleniurn
 Silver
 Trullium
Sort
Suharna Ingestion
mg/kg d
E1 ma
E 1 ma
Et ma
Et ma
El ma
E1 ma
El ma
El ma
Etma
El ma
El ma
Etma
E1 ma
El ma
E 1 ma
El ma
E1 ma
El mj
El nu
El ma
El ma
El ma
E 1 rna
El ma
El ma
El ma
El ma
El ma
E1 ma
El ma
El ma
El ma
El mai
El mai
El mai
El ma
El mat
El mai
E 1 ma>
E 1 mai
E 1 mai
El man
E 1 mai
E 1 "Ml
E 1 mai
< 1 BE 16
• 7 7E 16
« 73E16
1 2E 15
78E 16
8 96 15
42E-14
1 7E-15
49E-15
5 7E IS
1 IE 14
1 IE 14
26E IS
1 2E 14
70E 14
8 BE 15
1 IE 13
2 IE 13
34E 13
34E 13
40E 12
20E 11
1 3E 12
1 2E 11
70E 12
5 IE 13
IDE 14
1 9E 11
S3E 11
86E 13
1 9E 11
80E 12
1 2E 12
46E 11
5 7E 11
1 2E 13
68E 13
32E 12
20E 10
98E 10
4 7E 12
S 7E 10
43E 12
2 2E 10
3 IE It
Soil
Deimal
Conlacl
mg/kg d
9 7E 17
42E 16
40E 16
6 7E 16
42E 16
48E 15
2 3E 14
92E 16
2 7E 15
3 IE 15
6 IE 15
5 7E 15
1 4E 15
65E 15
3 8E 14
48E 15
70E 14
1 IE 13
1 9E 13
1 BE 13
4 4E 12
2 2E 11
1 5E 12
1 3E 11
7 7E 12
5 5E 13
1 IE 14
2 IE 11
5 7E 11
94E 13
2 IE 11
87E 12
2 2E 13
84E 12
1 OE 11
22E 14
1 2E 13
59E 13
3 7E 11
1 BE 10
86E 13
1 6E 10
78E 13
39E 11
55E 12
Boel
Ingiislion
mg/kg d
1 3E 13
2 1E 12
1 4E 12
3 7E 13
52E 13
42E 12
76E-10
40E 13
19E 12
1 1E 11
5 BE 12
1 IE 11
25E 12
7 1E 12
56E 12
t IE 12
63E 11
30E It
19E 11
49E 10
4 1E 08
24E 08
34E 06
1 8E 12
39E 09
92E 06
2 7E 11
26E 10
49E U
30E 12
1 5E 07
36E09
15E 11
2 7E 10
7 BE 11
1 5E 13
7 BE 12
20E 11
70E 11
1 2E 09
1 IE 10
54E 09
1 8E 10
8 1E 09
1 IE 10
Poik
Ingasl'on
mg/kg d
1 3E 14
t 7E 13
1 IE 13
3 ?E 14
'45E 14
3 IE 13
54E 11
37E 14
15E 13
BSE 13
54E 13
B7E 13
20E 13
6 IE 13
54E 13
12E 13
46E 12
90E 12
56E 12
40E 11
1 IE 09
8 OE 10
93E 08
29E 13
1 BE 10
25E 07
BOE 13
73E 11
1 7E 11
1 OE 12
3 7E 09
1 BE 10
24E 12
34E 11
1 4E 10
46E 14
1 4E 13
92E 12
70E 11
1 6E 09
1 9E 10
5 IE 08
1 7E 12
1 1E 08
t 2£ II
Chicken
Ingeslron
mg/kg d
66E 16
2 7E 15
1 2E 15
1 BE 15
1 5E 15
2 7E-15
1 9E 14
14E 15
3 IE 15
15E 14
22E 14
1 BE 14
43E 15
1 BE 14
24E 14
74E 15
22E 14
1 IE 12
64E 13
66E 13
6 1E 14
39C 13
3 IE 15
18E 15
4 IE 13
6 BE 13
22E 16
1 9E 13
45E 14
26E 15
7 BE 12
42E 13
25E 14
18E 11
73E 14
25E 15
BSE 13
1 5E 13
3 IE 09
4 3E 10
40E 13
2 3E 09
2 BE 14
3 IE 09
1 4E 11
Other
Poultry
Irigeslion
mg/kg-d
1BE 16
74E 16
34E 16
49E-16
40E-16
73E 16
50E-15
37E-16
83E-16
4 IE-IS
60E 15
49E 15
1 2E 15
49E IS
66E 15
20E 15
59E 15
29E 13
1 7E 13
18E 13
1 7E 14
IOE 13
84E 16
48E 16
1 1E 13
1 8E 13
59E 17
5 IE 14
1 2E 14
70E 16
2 IE 12
1 IE 13
67E 15
50E 12
20E 14
6 BE 16
22E 13
39E 14
83E 10
1 2E 10
1 1E 13
62E 10
75E 15
85E 10
39E 12
EOS
Ingnslion
mg/kg d
42E 16
1 7E 15
79E 16
1 2E 15
93E 16
1 7E IS
1 2E-14
86E 16
1 9E-1S
95E 15
1 4E 14
1 IE 14
27E 15
1 IE 14
15E 14
4 7E-15
14E 14
69E 13
4 1E 13
42E 13
35E 11
22E 10
1 BE 12
IDE 12
23E 10
39E 10
1 2E 13
1 IE 10
26E 11
1 5E 12
4SE09
24E 10
1 3E 13
1 IE 11
2 7E 11
1 4E 15
90E 15
1 1E 13
1 4E 09
1 7E 11
30E 13
1 1E 09
25E 13
1 4E 09
65E 12
Milk
fngaslion
rng/kg-d
22E 14
37E 13
25E 13
63E 14
89E 14
72E 13
t 3E 10
69E 14
32E 13
1 8E 12
IOE 12
19E 12
42E 13
1 2E 12
96E 13
19E 13
1 IE 11
49E 12
32E 12
BSE 11
37E 08
22E 08
3 IE 06
1 7E 12
34E 09
82E 06
24E 11
20E to
38E 11
24E 12
1 3E-07
32E 09
4 IE 12
22E 11
51E 10
37E 16
14E 12
14E 11
15E 10
42E 09
5 IE 11
22E 07
35E 09
1 OE 09
80E 11
Cheese
Ingaslion
rug/kg d
28E 14
48E 13
32E 13
83E 14
t 2E 13
94E 13
1 7E 10
90E 14
42E 13
24E 12
1 3E 12
24E 12
55E 13
16E 12
1 2E 12
25E 13
14E 11
65E 12
42E 12
1 IE 10
32E 09
19E 09
27E 07
15E 13
30E 10
72E07
2 IE 12
18E M
33E 12
20E 13
1 2E 08
2 BE 10
36E 13
19E 12
44E 11
32E 17
1 2E 13
1 2E 12
1 3E 11
3 7E 10
44E 12
19E 08
3 1E 10
9 IE 11
70E 12
Milk
Dessoits
Ingasliim
rng/kg d
1 5E 14
26E 13
1 7E 13
45E 14
63E 14
5 IE 13
93E 11
49E 14
23E 13
1 3E 12
7 IE 13
1 3E 12
30E 13
87E 13
68E 13
1 3E 13
77E 12
35E 12
23E 12
60E 11
40E 09
24E 09
3 3E 07
1 9E 13
37E 10
90E07
26E 12
22E 11
42E 12
26E 13
1 5E 08
35E-10
45E 13
24E 12
56E 11
40E 17
1 5E 13
t 6E 12
1 7E 11
46E 10
55E 12
2 4E 08
3 BE 10
1 IE 10
8 7E 1?
Yogurl
digestion
rnq/kg d
7 IE 16
1 2E 14
8 IE 15
2 IE 15
29E IS
23E 14
43E 12
22E 15
10E 14
60E 14
33E 14
6 1E 14
1 4E 14
40E-14
3 IE 14
62E IS
36E 13
16E 13
IOE 13
2 BE 12
1 2E 09
7 IE 10
1 OE 07
56E 14
1 IE 10
2 7E 07
7 7E 13
66E 12
1 2E 12
7 7E 14
44E 09
t OE 10
1 3E 13
72E 13
1 7E 11
12E 17
45E 14
4 7E 13
50E 12
1 4E 10
1 7E 12
7 3E 09
1 1E 10
3 4F 11
2 6F 12
Cream
Ingeslion
mg/kg d
59E 15
1 OE 13
6 7E 14
1 7E 14
24E 14
20E 13
36E 11
1 9E 14
8 7E 14
SOE 13
2 7E 13
5 IE 13
1 2E 13
33E 13
26E 13
5 IE 14
30E 12
1 3E 12
8 7E 13
2 3E 11
BOE 10
4 7E 10
66E 08
3 BE 14
75E 11
1 BE 07
52E 13
44E 12
83E 13
5 IE 14
29E 09
69E II
90E 14
4 BE 13
1 1E It
80E 18
SOE 14
3 IE 13
34E 12
9?E 11
1 IF 12
49F 09
7 6t 11
2 If 11
1 U 1?
Butter
Inqeslinn
mg/kg d
29E 14
49E 13
33E 13
BSE 14
1 2E 13
96E 13
I8E 10
92E 14
43E 13
25E 12
13E 12
25E 12
5 7E 13
1 6E 12
1 3E 12
25E 13
1 5E 11
66E 12
4 3E 12
1 IE 10
1 2E 09
7 IE 10
1 OE 07
56E 14
1 IE 10
2 7E 07
7 7E 13
66E 12
1 2E 12
7 7E 14
44E 09
IOE 10
1 3E 13
72E 13
1 7F It
1 2F 17
45E 14
4 7E 13
SOE 12
1 4F 10
1 n 12
7 )f 09
1 If 10
1 41 II
? M 1?
E«posod
Pioduce
digestion
mg/kg d
1 7E 16
29E IS
40E IS
1 3E 15
1 3E 15
65E 14
82E 12
24E IS
ME 14
1 9E 14
1 5E 14
3 IE 14
70E 15
2 3E 14
BOE 14
6 7E 15
1 BE 12
44E 14
4 4E 14
1 2E 12
1 4E 10
65E 11
7 2E 08
1 IE 09
6 BE 12
34E 10
6 2E 14
6 7E 12
29E 11
1 9E 13
3 BE 11
69E 12
69E 12
38E It
t 9E 10
25E 14
2 4E It
69E 13
56E 11
2 7F 08
2 IE 11
1 IF 09
6 OF 11
2 ){ II
3 41 ()•»
      ' V  Apn.-odii V 13
-------
M.II Cancel and NHxCDD
1 2.3,4,6.7.8 HpCDD
OCDO
23.7.8 TCDF
1. 2.3,7.8 PeCDF
2.3.4,7.8 PeCDF
1 2.3.4,7.8 HxCDF
1.2.3.6.7.»HxCDF
t 2.3.7.8.9 HxCDF
2 3.4.6.7.8 HxCDF
1 2,3.4.6.7.8 HpCDF
1 2.3.4.7.8.9 HpCDF
OCOF
T Mi achloi obtptwnyl
HexachkHobrphenyt
Hep(acMoiobipb*ny1
Bemo(a)pyiene
B«nio(b)flu«anllien«
Bis(2-«lhy1h«xy1)phlhalale
Caibon tetrachlofide
L>ib«u(»,h)anlhracene
Oi(n)oclv) phlhalale
Heplachkx
H*«achkxoberuene
HeiachkMobuladierw
Hexachtbfocyctopenladiena
Hexachtbrophena
lnd«no(1 .2,3-cd)pyiaM
Antimony
Arsenic
Barium
Ban/drum
Cadmium
Chiomium (haxavalanl)
Lead
Marcury
Nickel
Selenium
Silver
Thallium
Zinc
Subaiea
E t mai
E 1 man
El ma>
E 1 man
E 1 max
El max
E t max
Et max
El max
Et max
El max
E1 max
Et max
El max
Et max
E 1 ma.
E t max
El ma»
E 1 max
E1 max
Et max
Et ma
Et ma
Et ma
El ma
Et ma
Et max
Et max
Et max
Et max
Et max
El max
Et max
Et max
Et max
El max
Et max
El max
Et max
El max
El max
El max
El max
El mai
E f max
Piolecled
Produce
Ingeslion
rug/kg d
62E 18
2 7E 17
S4E-18
t BE 17
5 BE 18
38E-17
4 IE 16
69E 17
1 4E-16
1 4E-1B
16E-16
1SE-18
3 7E 17
1 7E 16
45E 16
5 7E 17
25E 16
20E 14
SBE IS
29E 15
2 7E 13
1 2E 12
1 BE 14
96E 10
2 2E 13
26E 15
55E 16
55E 12
24E-11
16E-13
20E-13
26E-13
37E 12
t 2E-11
78E-11
3 IE-IS
1 2E-11
20E 13
25E 11
23E 08
1 5E-11
68E 10
44E 11
S9E 13
29E 09
leafy
Produce
Ingeslion
mg/kg d
34E 15
62E 14
86E 14
23E 14
2 7E 14
t 4E 12
t 8E 10
5 IE 14
3 IE 13
42E-13
2BE-13
64E 13
15E 13
47E 13
1 SE 12
12E 13
3 BE 11
4SE 13
8 1E 13
26E 11
29EO9
1 4E«
1 66 06
25E 10
39E 12
74E 09
1 3E 12
76E 12
73E 12
1 3E-13
22E-11
39E-12
7 BE 12
34E-11
26E 10
1 7E 14
t 7E-11
35E-13
4 BE 11
35E-08
57E 12
35E 10
50E 11
1 3E 11
1 3E^»
Rool
Pioduce
Ingeslion
mg/kg-d
1 3E 17
56E 17
29E 17
67E 17
42E 17
2 BE 16
t 8E 15
1 3E 16
33E 16
36E 18
61E 16
57E-16
ME 18
6SE 16
2 7E IS
34E 16
30E 15
34E 13
S4E 14
32E 13
75E 14
33E 12
66E 14
2 7E 10
8 BE 13
83E 11
32E 14
30E 10
92E 11
44E 12
2 IE 10
97E 13
8 7E-15
BSE IS
1 4E-13
5 IE 19
42E 14
25E 17
32E 14
B6E 12
72E 16
1 9E 13
1 OE 13
63E 17
BSE 13
Exposed
Frurl
Ingeslion
mg/kg-d
1 4E 16
25E 15
34E 15
1 IE IS
1 IE 15
55E 14
70E 12
2 IE-IS
1 2E-14
1 7E-14
1 2E 14
26E 14
80E 15
20E 14
6 BE 14
5 7E 15
1SE 12
3 BE 14
3 7E 14
10E 12
1 2E 10
5SE 11
6 IE 06
9SE 10
SBE 12
29E 10
52E 14
5 7E 12
24E 11
1 6E-13
33E 11
S9E 12
59E 12
32E-11
1 6E 10
2 IE H
2 IE 11
S9E-13
4 BE 11
23E^M
1 BE 11
93E 10
52E 11
1 9E 11
29E 09
Piolecl«d
Fruil
Ingeslion
mg'kg d
15E 17
64E 17
1 3E 17
42E !7
14E-17
92E-17
9 BE 16
16E 16
33E 16
33E 16
39E 16
36E 18
8 BE 17
4 IE 16
1 IE 15
1 4E 16
60E 16
4 7E 14
1 4E 14
70E 15
64E 13
30E 12
44E-14
2 3E-09
53E 13
6 IE IS
1 3E IS
1 3E 11
59E 11
3 BE 13
4 BE 13
63E 13
8 BE 12
29E 11
1 9E 10
74E 15
29E-11
496 13
59E 11
55E08
36E 11
1 6E 09
1 OE 10
2 IE 12
69E 09
Rivet
Waler
Ingeslion
mg/kg d
BOE 22
35E-21
8 IE 22
31E-21
19E 21
4 3E 21
6 7E-20
BOE 21
20E-20
2 IE 20
2 BE 20
26E20
64E 21
30E-20
64E 20
BOE 21
1 7E 20
18E 18
1 SE 18
1 7E 18
22E 17
1 IE 16
37E 17
53E 16
45E 17
29E-18
56E 20
30E 18
35E 16
50E-18
20E-16
49E-17
72E-17
1 6E-1S
32E-15
t BE 18
6 BE 17
40E-17
25E-1S
54E 14
19E-16
22E 14
26E 16
20E 15
1 9E 15
River
Waler
Dermal
Contact
mg/kg-d
35E 18
1 2E 17
1 4E 17
24E 17
34E 17
1 2E 16
S2E 16
32E 17
97E 17
1 3E 16
2SE 16
2 3E 16
56E 17
26E 16
1 2E 15
1 5E 16
t IE 15
47E 15
1 2E 14
25E 14
66E 14
3 BE 13
29E 13
t 3E-14
2 BE 13
7 BE 14
90E 17
SOE 13
1 2E-13
40E 15
20E-12
30E-13
26E 17
5 7E 16
1 2E-15
66E-19
25E-17
15E-17
89E 16
20E 14
68E 17
B2E 15
93E 17
73E 18
67E 16
Lake
Waler
Ingeslion
mg/kg-d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Walei
Dermal
Contact
mg/kg-d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Infant
Breast milk
Ingnstlon
ing/kg d
1 4E 13
23E 12
16E 12
42E-13
SBE 13
54E 12
93E 10
47E 13
22E 12
12E 11
6SE-12
1 2E 11
2 BE 12
BOE 12
7 IE 12
1 3E 12
92E 11
37E 11
24E 11
55E 10
2 7E 07
20E-07
4 1E-06
7 1E-12
97E08
5 2E 03
24E 10
1 9E-09
70E-11
8 7E-12
26E-05
82E-08
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Appnndu V  11
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Ma< Cancel and Nnni am 01 tiposi

Chemical

2 3.7.8 TCOO
1 2 3.7.6P»CDO
1 234.7.8HxCDD
123678 HiCDO
1.2.3.7 8.9 HxCDD
l.2.3.4.6.7.B-HpCOO
OCOD
2.3.7.8TCDF
1, 2,3.7.8 PeCOf
2.3.4.7.8 P«CDF
1 2 3 4.7.8 HxCDF
1 2.3 6.7.8 HxCDF
1 2 3 7,8.9 HxCDF
7 3 4.6.7.8 HuCDF
1 2.3.4.6.7.6 HpCDF
1 2.3,4.7.8.9 HpCDF
OCDF
T etlachloiobtphenyl
Hexachlorobiphenyl
Heptachtoiobiphenyl
Beruo4a)pyf0ne
Beruo(b)fluoiantt>en»
Bu(2 «1hy1he«yl)phlhalale
Caibon laliachloiide
Dibenj (a ,h)anlhi acene
Di(n)octyt pMhalal*
Heptachtoi
H««»chlo4ob«iuen«
HexachJoiobuladmne
HeiachkMocYClopenladiena
Heiachkxophene
lnd«ho(1 .2,3-cd)pyi»n«
Antimony
Aisanic
Baiium
Beryllium
Cadmium
Chiomium (hmavaktnt)
Lead
Mercury
Nickel
Selenium
Silvei
Thallium
2 me

Subaiea

El man
E 1 man
El man
El man
El man
El max
El mai
El max
El man
Et man
Et man
El man
Et man
Et ma>
E 1 max
El ma»
El man
E 1 niai
El mai
Et man
Et ma>
E1 ma>
E t mai
Et man
Et tnai
Et mai
El ma«
Et man
Et man
El mai
Et man
Et ma>
Et max
Et max
El max
Et max
El max
El max
Et mai
Et max
Et man
E1 max
E 1 max
E 1 mai
E 1 max
AVERAGE DAILY DOSE
Piolected I ejly
Pioduce
Ingeslion
mg/kg d
22E 17
94E-17
1 9E-17
62E 17
20E-17
1 3E 16
t 4E 15
2 4E-16
49E-16
4 BE- 16
see ie
53E-18
1 3E 16
60E 18
t BE 15
JOE 16
8 BE 16
69E t4
2 IE 14
IDE 14
94E 13
4 IE 12
64E 14
33E 09
7 7E 13
90E 15
t 9E 15
t 9E 11
B6E-11
55E 13
7 1E 13
92E-13
1 3E 11
42E-11
27E 10
1 IE 14
42E-11
7 IE 13
86E 11
8 IE 08
53E 11
24E4»
t 5E 10
3 1E 12
t OE 08
Pioduce
Ingeslion
mg/kg d
1 2E 14
22E-13
306-13
8 1E-14
93E-14
49E-12
63E-10
18E-13
1 IE 12
15E-12
98E 13
23E-12
5 IE 13
16E 12
53E 12
4 IE 13
t 3E tO
t 6E 12
28E 12
92E It
t OE 08
49E 09
55E 06
86E tO
1 3E 11
26E 08
4 7E 12
26E It
26E It
45E 13
7 BE 11
1 4E 11
27E 11
1 2E 10
90E-10
6 IE 14
60E 11
1 2E 12
1 7E 10
1 2E 07
20E It
12E09
t 8E 10
45E 11
45E 09
(ADD) FOR CHEMICALS WITH NONCARCINOGENIC HEALTH EFFECTS
Rivet Lake
Ron! E«posed Piolecled Rival Walei Lake Walei
Pioduce
Ingeslion
mg/kg d
46E 17
20E 16
IDE 16
24E 18
15E 16
99E 16
65E 15
46E 16
1 2E-15
13E 15
2 IE 15
20E 15
49E 16
23E 15
93E 15
1 2E IS
1 OE 14
1 2E 12
1 9E 13
t IE 12
26E 11
1 IE 11
2 3E 13
93E 10
3 IE 12
22E to
1 IE 13
t IE 09
32E 10
1 5E 11
73E 10
34E 12
30E 14
30E 14
49E 13
18E 18
15E-13
89E 17
1 IE 13
30E 11
25E IS
68E 13
36E 13
22E 16
30E 12
Fiurt
Ingeslion
mg/kg -d
50E 16
86E IS
t 2E 14
3 BE 15
40E 15
1 9E-13
24E 11
72E 15
43E-14
5 BE 14
43E-14
92E 14
2 IE 14
69E 14
24E 13
20E 14
53E 12
1 3E 13
1 3£ 13
35E 12
4 IE 10
t 9E 10
2 IE 07
33E09
20E 11
10E49
1 BE 13
20E 11
66E 11
56E 13
1 IE 10
20E 11
2 1E-11
1 IE 10
56E-10
74E 14
72E 11
2 IE 12
1 7E 10
82E08
62E 11
33E09
1 BE 10
6 BE It
1 OE 08
Fiuil
Ingeslion
mg/kg d
52E 17
22E 16
46E 17
15E 16
49E-17
32E-16
34E-15
5 7E-16
1 2E 15
1 IE-IS
1 3E-15
1 3E 15
3 1E 16
1 4E 15
3 BE 15
4 BE 16
2 IE 15
1 7E 13
SOE 14
25E 14
22E 12
10E 11
1 5E 13
aOE 09
t BE 12
2 IE 14
46E 15
4 BE 11
20E 10
1 3E 12
1 7E 12
22E 12
3 IE 11
IDE 10
65E 10
26E 14
10E-10
1 7E 12
2 IE 10
1 9E 07
1 3E 10
S7E 09
36E 10
74E 12
24E OB
Walef
Ingeslion
mg/kg-d
2 BE 21
1 2E 20
2 BE 21
1 1E 20
6 BE 21
1 5E-20
23E-19
2 BE 20
70E 20
7 4E-20
9 BE 20
9 2E 20
2 2E 20
10E 19
22E 19
2 BE 20
59E 20
63E 18
52E IB
6 IE 18
79E 17
3 BE 16
1 3E 16
19E 15
16E 16
IDE 17
20E 19
1 IE t5
1 2E 15
18E 17
6 BE 16
1 7E-16
2SE-16
S5E-15
1 1E-14
64E-1B
24E-16
14E 16
B6E 15
19E 13
66E 16
79E 14
89E 16
7 IE 15
6SE 15
Dei mai
Conlacl
mg/kg-d
1 2E 17
4 IE 17
50E 17
BSE 17
1 2E-16
4 IE 16
18E 15
1 1E-16
34E 16
44E 16
86E 16
8 IE 16
20E 16
92E 16
4 IE 15
5 IE 16
37E 15
1 7E 14
40E 14
86E 14
23E 13
1 3E 12
10E 12
44E 14
10E 12
27E 13
32E 16
1 7E 12
4 IE 13
14E 14
71E-12
10E 12
9 IE 17
20E-15
4 IE-IS
23E IB
87E-17
5 IE 17
3 IE 15
69E 14
24E 16
29E 14
32E 16
26E IS
24E 15
Walei
Ingestion
mg/kg-d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Dermal
Conlacl
mg/kg-d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Volume V Aiip«ndi« V I1
-------
                            APPENDIX V-14

            Estimation of Inhalation Cancer Risks and Hazard Quotients
Volume V
Appendix V-14
-------
 TABLE 3  Average Inhalation Risks and Noncanccr HQs in Subarca F3
CHEMICAL
Dichlorodifluoromethane
Dichlotoelhane. 1.1- (Ethyltdone dichloride)
Dichloroethane, 1.2-
Dichloroothene. 1,1- (Vmylidine chloride)
Dlchloroethene (Irani). 1 .2-
Dichlorophenol. 2.4-
Dichlocopropane, 1 ,2- (Propylene dichloride)
Dlchlofopropene (els). 1.3-
Dlchloropropene (trans), 1 ,3-
Diethylphthaiato
Dlmethoxybenzldlne. 3,3'-
Dlmettiylpheno). 2,4-
Dimettiylphthalate
Dl n-butylphthalate
Dlnrtrololuene. 2,6
Dlnrtro-2-methylphenol. 4.6-
Dlnttrophenol. 2.4-
DlnKrololuene. 2.4-
Dloxane. 1.4-
Di(n)octyl phthalale
D, 2,4-
Ethyl methicrylste
Ethylbenzene
Ethylene dibromlde
Ethylene oxide
Ethylene thlourea
Fluoranthene
Fluorene
Formaldehyde
Furfural
Hepfachlor
Heptachloroblphenyl
Hexachlorobenzane
Hexachlorobiphenyl
Hexachlorobutadiene
Hexachlotocyclohexane. gamma (Llndane)
Hexachlorocyclopentadiene
Hexachloroe thane
Hexachlorophena
Hexanone. 2-
lndeno(1 .2.3 cd)pyren«
IsophoronB
Maleic hydrazide
Methoxychlor
Methyl t butyl ether
Methyl-2-Pentanone. 4 (MIBK)
Methylene chloride
Methytnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nrtroamhne 2-
Nitroanihne. 3-
Inhalation
Slope
Factor
(mg/kg-d)«-1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E-01
NA
NA
NA
45E 02
NA
45E+00
NA
1 6E+00
NA
7 8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E 03
NF
NA
NA
NA
NF
RAC
(m(j/m3)
005
0 125
NA •'
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E-02
3 6E-02
. NA
2 3E 03
50E03
7 5E 04
2 9E-04
1 4E-03
1 4E 03
20E-01
NA
50E-03
NA
2 5E 02
2 5E-04
NF
50E-04
5 OE-04
NA
50E03
2 5E 03
2 3E 02
7 IE 02
1 4E-05
NA
2 OE-05
1 OE 02
1 OE 02
50E02
3 6E 03
1 3E-04
NA
2 OE-04
NA
50E05
7 5E 05
50E-06
2 5E 04
7 5E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E 04
3E 05
3E-05
3E 05
3E 05
55E 06
3E05
, 3E-05
3E-05
7E-05
2E-04
55E-06
55E-06
1 6E-05
55E-06
55E-06
55E 06
55E-06
49E04
55E-06
39E-05
2 5E-04
5 OE-04
1 2E-04
3 IE-OS
1 5E-10
55E-06
87E-06
6 IE -04
55E-06
55E-07
1 4E-08
55E-06
1 4E-08
1 OE-04
55E-05
55EO6
55E-06
32E05
64E-05
55E-06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subaiea
E3 avg
E3 avg
E3avg
E3 svg
E3 avg
E3avg
E3avg
E3 avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3 avg
E3avg
,' E 3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3avg
E3 avg
E3 avg
Adult
Cancer
Risk
NT
NT
24E 12
32E-11
NT
NT
NT
34E-12
34E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
23E-11
NT
NT
NT
58E-11
NT
52E-12
NT
1 9E-11
NT
1 7E-11
NT
NT
1 6E-13
NT
NT
NT
NT
NT
NT
W
NT
1 4E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
60E 12
79E 11
NT
NT
NT
BSE 12
85E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
rn
NT
46E 10
56E-11
NT
NT
NT
1 4E-10
NT
1 3E-11
NT
47E-11
NT
4 1E-11
NT
NT
4 1E-13
NT
NT
NT
NT
NT
NT
NT
rn
34E-12
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
36E 12
48E-11
NT
NT
NT
5 IE 12
51E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E-10
34E-11
NT
NT
NT
87E-11
NT
79E-12
NT
28E-11
NT
25E-11
NT
NT
24E-13
NT
NT
NT
NT
NT
NT
NT
tJT
2 1E-12
NT
NT
NT
ra
NT
Farmer
Cancer
Risk
NT
NT
53E 12
70E-11
NT
NT
NT
76E-12
76E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
WT
NT
NT
41E-10
5 OE-1 1
NT
NT
NT
1 3E-10
NT
1 2E-11
NT
42E-11
NT
37E-11
NT
NT
36E-13
NT
NT
NT
NT
NT
NT
in
rn
3 1E-12
NT
NT
NT
NT
NT
                                                                                                                                               Adult      Child    School age  Farmer
                                                                                                                                             Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                                HQ        HQ        HO        HQ
2 8E-07
5 BE -09
NT
9 IE -08
4 IE 08
1 2E 07
7 2E 07
1 4E 07
1 4E-07
1 4E-09
NT
1 BE -08
NT
1 OE-08
3 6E-07
NT
1 BE 07
1 8E^)7
NT
1 8E-08
26E-07
1 8E^>7
1 1E^)7
1 3E4)4
NT
1 2E-10
90E-09
1 1E-06
2 OE 07
2 5E-08
7 2E-08
NT
45E-07
NT
33E-05
1 2E-05
1 BE -05
3 6E 07
70E-06
NT
NT
22E^)9
1 5E-08
72E-09
96E-10
36E 08
3 OF. 08
NT
HI
90E 09
7 7f 06
rn
1 1E-06
2 1E-08
NT
34E 07
1 5E-07
45E 07
27E-06
54E-07
54E 07
52E-09
NT
68E 08
NT
3 BE 08
1 4E-06
NT
68E47
6 BE -07
NT
6 BE 4)8
9 5E-07
6 7E-07
43E 07
49E-O4
NT
45E-10
34E 08
4 IE 08
75E-07
9 5E 08
2 7E-07
NT
1 7E-06
NT
1 2E 04
45E 05
6 BE -05
1 4E 06
26E 05
NT
NT
8 2E 09
56E 08
2 7E 08
3 BE 09
1 IT 07
t tr 07
rn
rn
3 4F 08
? 'ti m
rn
64E-07
1 3E-08
NT
2 1E-07
9 3E 08
2 7E-07
16E 06
3 2E 07
32E-07
3 1E-09
NT
4 1E-08
NT
2 3E-08
8 2E 07
NT
4 IE 07
41E-07
NT
4 IE 08
5 BE -07
40E^)7
26E-07
3 OE-04
NT
27E-10
20E08
25E 08
4 5E-07
5 7E-08
1 6E-07
NT
1 OE-06
NT
75E05
2 7E-05
4 IE 05
82E 07
1 6E-05
NT
NT
50E 09
34E 08
1 GE 08
2 2E 09
8 IE 08
6 9F OB
NT
rn
20E 08
1 7E 05
rn
2 BE 07
5 BE -09
NT
9 IE 08
4 IE 08
1 2E 07
7 2E 07
1 4E 07
1 4E-07
1 4ErJ39
NT
1 8E-OB
NT
1 OE 08
36E-07
NT
1 BE 07
1 BE -07
NT
1 BE -06
2 6E 07
1 BE 07
1 IE 07
1 3E 04
NT
1 2E 10
90E 09
1 IE 08
2 OE 07
25E08
7 2E 08
NT
4 5E 07
NT
3 3E 05
1 2E 05
T BE 05
36E 07
7 OE-06
NT
NT
22E 09
1 5E 08
72E 09
96E 10
36E 08
3 OF 08
NT
NT
90E 09
7 7E OB
NT
Volume V. Appendix V-14
-------
TABLE 3  Average Inhalation Risk1; and Noncancer HQs in Subarpa F 3
CHEMICAL
Niboaniline, 4-
Nrtrobenzene
Nrtrophenol. 2-
Nrtrophenol, 4-
N-Nitioso-di-n-butytamlne
N Nitroso-di n-propylamine
N-Nitrosodiphenylamlne (Diphenylamine)
Nonachroroblphenyt
Octachlofobtphenyt
Pentachlorobenzene
Pentachloroblphenyl
Pentachlofonitrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl)-1.3 benzodioxole)
Styrene
Tetrachloroblphenyl
Tetrachloroethane. 1.1.1.2-
Tetrachloroethane. 1,1.2,2-
Tetrachloroethene
Tetrachloropheno). 2.3.4.6-
Toluene
Trichloro-1,2,2-trrfluoroethane, 1.1.2
Trichlorobenzene. 1.2,4-
Trichloroblphenyl
Trichloroethane, 1.1,1- (Methyl chlorotorm)
Trichloroethane. 1.1.2-
Trlchloroethene
Trichlorofluoromethane
Trichlorophenol. 2.4.5-
Trichlorophenol. 2,4.6-
Vmyl acetate
Vinyl chloride
Xylene, m/p- (m/p-Dimethyt benzene)
Xylene, o- (o-Dimethyl benzene)
2.3.7.8-TCDD
l!2!37.8PCDD
1 234.7.8 HxCDD
1.2.3.6.7.8 HxCDD

1 2 3 4 6 7.8 HpCDD
OCDD
2 3 7.8-TCDF
1 2 3.7.8 PCDF
234 7.8 PCDF
12347 8 HxCDF
1 2 3 6.7.8 HxCDF
234678 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)"- 1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E-02
2 OE-01
2 OE-03
NA
NA
NA
NA
NA
NA
5 7E-02
6 OE-03
NA
NA
10E-02
NA
3 OE-01
NA
NA
1 5E+05
75E+04
1 5E+04
1 5E*04
1 5E404
1 5E*03
1 5E+02
1 5E+04
7 5E+03
75E»04
t 5E«04
1 5E*04
1 5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
tJA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E-04
7 5E-03
NA
1 5E-01
75E-03
NF
7 1E-02
NA
7 5E-03
NA
2 5E-03
7 5E 03
2 9E-02
2 1E»00
1 4E-02
NA
7 1E-02
1 OE-03
NA
5 OE 02
2 5E-02
NA
1 4E-02
NA
5 OE-01
5 OE-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rats
(g/sec)
67E-06
55E 06
67E-06
55E-06
1 2E-04
67E-06
67E-06
1 4E 08
•1 4E-08
48E-05
1 4E-08
34E-05
55E-06
67E-06
55E-06
55E06
1 2E-04
23E-05
1 4E-08
55E-06
55E-06
5 1E-05
68E-06
6 1E-04
3 3E-04
55E-06
30E-OB
1 3E-05
1 3E-05
1 9E 05
2 5E-04
55E06
55E06
64E-05
2 5E 04
3 8E 04
55E06
1 08E 11
6 78E 11
8 95E 1 1
1 66E 10
1 09E 10
1 24E 09
6 15E 09
877E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
E3avg
E3avg
E3avg
E3avg
E3>vg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3»vg
E3avg
E3avg
E3avg
E3«vg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3 avg
E3avg
E3 avg
E3avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3avg
E3 avg
E3 avg
E3 avg
Off site
Vapor
Cone
(ug/m3)
40E-07
3 3E-07
40E 07
3 3E 07
7 3E-06
40E-O7
40E-07
84E-10
84E-10
29E-06
84E-10
20E-06
33E-07
40E-07
3 3E-07
3 3E-07
69E06
1 4E-06
84E-10
33E417
33E-07
31E-06
4 1E-07
37E-05
20E-O5
3 3E-07
1 BE -09
7 5E-07
7 5E-07
1 1E-06
1 5E-05
33E-07
33E07
3 9E-06
1 5E-05
2 3E 05
33E-07
65E-13
4 IE 12
54E 12
99E 12
65E-12
74E 11
3 7E 10
53E 12
2 IE 11
2 BE 11
86E 11
80E 11
9 OE 1 1
Cancer
Adult
Dose
(mg/kg-d)
1 4E-11
1 2E-11
1 4E 11
1 2E-11
26E 10
1 4E-11
14E-11
30E-14
30E-14
1 OE-10
30E-14
7 1E-11
12E-11
1 4E-11
1 2E-11
1 2E-11
24E-10
48E-11
30E-14
1 2E-11
1 2E-11
1 1E-10
1 4E 11
13E-09
7 OE-10
1 2E-11
64E-14
26E-11
26E-11
39E-11
52E-10
12E-11
1 2E-11
1 4E-10
52E-10
8 OE-10
1 2E-11
23E 17
1 4E 16
1 9E 16
35E 16
2 3E 16
26E 15
1 3E 14
» 9E 16
7 3E 16
99E 16
30E 15
2 BE 15
3?E 15
Cancer
Child
Dose
(mg/kg-d)
35E 11
29E-11
35E 11
29E 11
64E-10
35E-11
35E-11
74E 14
74E-14
25E-10
74E-14
1 8E-10
29E-11
35E-11
29E-11
29E-11
6 1E-10
1 2E-10
74E-14
29E-11
29E-11
27E 10
36E-11
32E-09
1 7E 09
29E-11
1 6E-13
66E-11
66E-11
98E-11
1 3E-09
29E-11
29E-11
34E-10
13E-09
20E09
29E-11
57E-17
36E 16
4 7E 16
87E-16
5 7E 16
65E 15
32E 14
46E 16
1 BE 15
25E 15
75E 15
70E 15
79E 15
Cancer
School-age
Dose
(mg/kg-d)
2 1E-11
1 7E-11
2 IE 11
1 7E 11
38E 10
2 IE 11
2 IE 11
45E-14
45E 14
1 5E-10
45E-14
1 1E-10
1 7E-11
2 1E-11
1 7E-11
1 7E-11
37E-10
72E-11
45E-14
1 7E-11
1 7E-11
1 6E-10
22E 11
1 9E-09
10E-09
1 7E-11
96E-14
40E-11
40E-11
59E-11
78E-10
1 7E-11
1 7E-11
2 OE-10
78E-10
1 2E-09
1 7E-11
34E-17
22E 16
28E 16
53E 16
35E 16
39E 15
20E 14
28E 16
1 IE 15
1 5E 15
4 5E 15
42E 15
4 8E 15
Cancer
Farmer
Dose
(mg/kg d)
3 IE 11
26E 11
3 1E-11
26E 11
5 7E-10
3 IE 11
3 IE-It
66E-14
66E-14
22E 10
66E-14
1 6E-10
26E-11
31E-11
26E-11
26E-11
54E-10
1 IE 10
66E-14
26E-11
26E-11
24E-10
32E-11
29E-09
1 5E-09
26E-11
1 4E 13
59E 11
59E 11
8 BE 11
1 2E 09
26E-11
26E-11
3 OE-10
1 2E-09
1 8E 09
26E-11
5 IE 17
32E 16
42E 16
7 BE 16
5 1E-16
5 BE 15
2 9E 14
4 1E 16
1 6E 15
2 2E 15
6 7E 15
6 3E 15
7 IE IS
Noncancer I
Adult
Dose
(mg/kg d)
1 IE 10
90E 11
1 IE 10
90E 11
2 OE 09
1 IE 10
1 IE 10
23E 13
23E 13
7 BE 10
23E 13
55E-10
90E-11
1 IE 10
90E 11
90E 11
19E 09
37E-10
23E 13
90E-11
90E-11
84E-10
1 1E-10
1 OE-08
54E09
90E-11
50E-13
2 1E-10
2 IE 10
3 IE 10
40E09
90E-11
90E-11
1 1E-09
40E 09
6 2E 09
90E-11
1 8E 16
t IE 15
1 5E 15
2 7E 15
1 8r 15
20E 14
1 OE 13
1 4E 15
5 7E 15
7 7E 15
2 3E 14
2 2E 14
2 f>F 14
Moncancer 1
Child !
Dose
(mg/kg d)
4 IE 10
34E-10
41E-10
34E 10
7 4E-09
4 IE 10
4 IE 10
86E-13
86E-13
29E09
86E-13
2 1E-09
34E 10
4 1E-10
34E-10
34E 10
7 IE 09
1 4E-09
86E 13
34E 10
34E-10
31E-09
42E 10
3 BE 08
20E 08
34E 10
1 9E 12
77E-10
7 7E 10
1 1E-09
1 5E 08
34E-10
34E 10
39E 09
1 5E 08
2 3E 08
34E 10
66E 16
42E 15
55E 15
1 Of 14
6 7E 15
76E 14
3 BE 13
54E 15
2 IE 14
29E 14
8 BE 14
82E 14
9 ?F 14
Moncancer 1
5chool-age
Dose
(mg/kg d)
25E-10
20E 10
25E-10
2 OE-10
4 5E 09
25E 10
2UE 10
52E-13
52E-13
18E-09
52E-13
1 3E-09
2 OE-10
25E 10
2 OE-10
2 OE-10
43E-09
83E-10
52E 13
20E 10
2 OE-10
1 9E-09
25E-10
2 3E 08
1 2E-08
20E 10
1 1E-12
46E 10
46E-10
69E 10
91E09
20E 10
2 OE-10
24E09
9 1E 09
1 4E 08
20E 10
40E 16
25E 15
3 3E 15
6 IE 15
40E 15
46E 14
2 3E 13
33E 15
1 3E 14
1 7E 14
53E 14
50E 14
5 fiF 14
Noncancer
Farmer
Dose
(mg/kg d)
1 IE 10
90E-11
1 IE 10
90E-11
20E 09
1 IE 10
1 IE 10
23E 13
23E 13
78E 10
j^SE-IS
55E-10
90E-11
1 lE-tO
90E-11
90E-11
1 9E-09
3 7E-10
23E-13
90E-11
90E 11
84E-10
1 1E-10
1 OE-O8
54E 09
90E-11
50E-13
2 IE 10
2 1E-10
31E-10
40E09
90E 11
90E-11
1 IE 09
40E09
62E 09
90E 11
1 BE 16
1 IE 15
1 5E 15
2 7E 15
1 BE 15
20E 14
1 OE 13
1 4E 15
5 7E 15
7 7E 15
23E 14
2 2E 14
? 5F 14
Volume V. Appendix V    \
-------
TABLE 3  Average Inhalation Risks and Noncancer MQs in Suhaica F 3
CHEMICAL
Nrtroaniline. 4-
Nrtrobenzene
Nitrophenol. 2-
Nittophenol. 4-
N Nrtooso-dl-n-butylamlne
N Nrtroso-dl-n-propylamlne
N Nrtrosodiphenylamine (Diphenylamlne)
Nonachk>foblph«ny)
Octachloroblphenyl
Pentachlorobenzene
Pentachloroblphenyl
PentachloronRrobenzene
Pantachlorophanol
Phenanthrene
Phono)
Pyrena
Safrole (5-(2-Propenyl)-1 ,3-beruodioxole)
Styrane
Tetrachlotoblphanyl
Tetrachlofoethane. 1.1 1.2
Tebachloroothane, 1,1.2.2-
Tetrachloroethene
T«bachlotophenol. 2.3,4.6
Toluene
Trichlofo- 1.2.2 -bifluofoethane. 1.1.2-
Trichloroberuene. 1.2,4-
Trlchloroblphenyl
Trlchloroathana. 1.1,1- (Methyl chloroform)
Trlchloroethane, 1.1.2-
Trichloroethene
Trlchlorofluoromethane
Trlchlorophenol. 2.4.5-
Trichlorophenol. 2,4.6-
Vlnyl acetate
Vinyl chloride
Xylene, m/p- (m/p Dimethyl benzene)
Xylene. o (o Dimettiyt benzene)
2.3.7.8TCDD
1.2.3.78PCDD
1.2.3.4.7.8HxCDD
1 .2 3 6 7 8 HxCDD
1,2,3.7.B.9HxCDD
1.2.3.46.78HpCDD
OCOD
2,3.7.8 TCDF
1.2 3.7,8 PCDF
23478PCDF
1.2,34,7.8HxCDF
12367 8 HxCDF
2 3 4 6. 78 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)"-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
60E-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E+05
75E+04
1 5E»04
1 5E«04
1 5E+04
1 5E+03
1 5E+02
1 5E»04
75E+03
75E»04
1 5E*04
1 5E+04
1 5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
0 1
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RtD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E 04
75E-03
NA
1 5E 01
7 5E-03
NF
7 1E-02
NA
75E-03
NA
25E 03
75E-03
29E-02
2 1E»00
1 4E-02
NA
7 1E 02
1 OE-03
NA
5 OE-02
25E-02
NA
1 4E-02
NA
5 OE-01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
Emission
Rate
(g/sec)
67E 06
55E-06
6 7E-06
55E 06
1 2E 04
6 7E-06
67E-06
•1 4E-08
1 4E-08
48E-05
1 4E46
34E-05
55E-06
87E^)6
55E 06
55E 06
1 2E 04
2 3E-05
1 4E 08
55E^»
55E-06
5 IE 05
68E06
6 IE 04
33E^>4
55E 06
30E^8
1 3E^)5
1 3E 05
1 9E-05
25E-04
55E 06
55E-06
64E-05
2 5E 04
3 8E-04
55E-06
1 08E-11
678E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E-10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
E3 avg
E3avg
E3 avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3tvg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3 avg
E3avg
E3 avg
E3avg
E3 avg
E3 avg
E3avg
E3 avg
E3avg
Adult
Cancer
Risk
NT
NT
NT
NT
1 4E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E-13
24E-12
22E-13
NT
NT
NT
NT
NT
NT
1 5E-12
23E-13
NT
NT
1 2E-13
NT
1 6E-10
NT
NT
34E 12
1 IE 11
2 BE 12
52E 12
35E 12
39E 12
1 9E 12
28E 12
55E 12
74E 11
45E 11
42E 11
48E 11
Child
Cancer
Risk
NT
NT
NT
NT
34E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
75E-13
59E-12
55E-13
NT
NT
NT
NT
NT
NT
37E-12
58E-13
NT
NT
29E-13
NT
39E-10
NT
NT
BSE 12
2 7E-11
7 IE 12
1 3E 11
86E 12
9 BE 12
49E 12
69E 12
4E 11
8E 10
IE 10
IE 10
2E 10
School age
Cancer
Risk
NT
NT
NT
NT
2 1E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
45E 13
36E-12
33E-13
NT
NT
NT
NT
NT
NT
23E-12
35E-13
NT
NT
1 7E-13
NT
2 3E-10
NT
NT
52E 12
16E 11
43E 12
79E 12
52E 12
59E 12
29E 12
42E 12
82E 12
1 IE 10
68E 11
64E 11
72E 11
Farmer
Cancer
Risk
NT
NT
NT
NT
3 1E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
67E 13
52E 12
49E-13
NT
NT
NT
NT
NT
NT
33E 12
52E-13
NT
NT
26E-13
NT
35E-10
NT
NT
76E 12
24E It
63E 12
1 2E 11
7 7E 12
87E 12
4 3E 12
62E 12
1 2E 11
1 6E 10
1 OE 10
94E 11
1 IE 10
                                                                                                                                               Adult     Child   School age   Farmer
                                                                                                                                             Noncancer Noncancer Noncancer  Noncancer
                                                                                                                                                HQ       HQ        HQ        MQ
NT
6 3E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
7 4E-07
1 2E-08
NT
60E-10
1 2E-08
NT
52E-09
NT
1 2E-08
NT
34E-07
1 5E 08
3 5E-07
25E09
63E-09
NT
29E 09
2 1E-07
NT
8 IE 08
36E 09
NT
74E-08
NT
1 2E 08
1 8E-10
NT
NT
NT
NT
NT
fJT
NT
(IT
111
NT
111
in
nr
NT
24E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 BE 06
4 5E 08
NT
23E 09
4 5E-08
NT
1 9E 08
NT
45E-08
NT
1 3E 06
56E 08
1 3E 06
95E09
2 4E 08
NT
1 IE 08
7 7E 07
NT
30E 07
1 4E-08
NT
2 BE 07
NT
4 7E 08
68E 10
NT
m
NT
NT
III
III
III
III
in
m
MI
m
NT
NT
1 4E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 06
2 7E-08
NT
1 4E 09
2 7E-08
NT
1 2E-OB
NT
27E-08
NT
76E 07
3 4E 08
80E07
5 7E 09
1 4E-08
NT
65E 09
46E^)7
NT
1 BE 07
82E 09
NT
1 7E-07
NT
28E 08
4 IE 10
NT
NT
NT
NT
NT
NT
NT
flT
NT
flT
HT
flT
rn
NT
63E-07
NT
NT
NT
NT
NT
NT
NT
NT,
NT
74E07
1 2E-08
NT
60E 10
1 2E-08
NT
52E-09
NT
1 2E 08
NT
3 4E 07
1 5E 08
35E07
25E09
63E 09
NT
29E09
2 1E-07
NT
8 IE 08
36E09
NT
7 4E 08
NT
1 2E 08
18E 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
tIT
NT
flT
-------
 TABl E 3 Average Inhalation Risks and Noncancer HQs in Subatca F3
CHEMICAL
1.2.3.7.8.9-HxCDF
t 234678 HpCDF

1.2.3.4. 7.8.9 HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Particulate matter
Resplrable participates
Inhalation
Slope
Factor
(mg/kg-d)"- 1
1 5E+04
1 5E+03

1 5E*03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA

NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA

NA
NA

NA
1 OE-04
75E05
36E05
1 3E 03
1 3E-04
1 3E 03
2 5E-01
NA
NA
21E05
50E 03
1 3E 03
1 3E 03
1 BE 05
75E 02
50E 04
NA
NA
NA
NF
Emission
Rate
 Not applicable
  NF ° Not found
  NT = No toxtcity information
  HQ » Hazard quotient
  HI = Hazard Index
Volume V, Appendix
-------
TABLE 3 Average Inhalation Risks and Noncancer HQs in Subaicn F_3
CHEMICAL
1237 8.9 HxCDF
1 234,6,78HpCDF
1, 2.3.4.7.8,9 HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsenic
Barium
Ban/Ilium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Respirable particulates
Inhalation
Slope
Factor
(mg/kg d)"-1
1 5E+04
1 5E«03
1 5E*03
1 5E»02

MA
NA
SO
NA
84
81
41
NA
NA
NA
NA
OB4
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
N/
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
HA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
1 OE 04
7 5E 05
36E-05
1 3E-03
1 3E-04
1 3E-03
2 5E-01
NA
NA
2 IE 05
50E03
1 3E-03
1 3E 03
1 BE 05
75E 02
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
2 93E-10
9 30E-09
1 22E-09
1 89E 08
4 2BE 08
24E 04
42E-08
37E-05
1 5E-04
33E08
16E05
7 1E-07
7 1E4)7
94E 05
43E 05
1 4E 03
50E 06
47E 04
1 5E 05
34E 05
1 2E 04
3 2E-02
24E»00
9 IE 02
72E 02
72E 02
Subaiea
E3 avg
E3 avg
E 3 avo
E3 avg

E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avj
E3avg
Adult
Cancer
Risk
9 3E-12
2 9E-1 1
3 9E-12
60E 12
30E 10
NT
NT
39E-09
NT
59E-13
2 IE 10
6 IE 11
NT
NT
NT
NT
89E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
7 IF 1 1
t, JC. - 1 1
7 3E-1 1
9 6E - 1 2
1 5E 11
74E 10
NT
NT
97E-09
NT
15E 12
5 IE 10
1 5E-10
NT
NT
NT
NT
22E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
1 
-------
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-------
TABLE t  Average Inhalaimn Risks and Noncancer MOs in Subjrea F 1
CHEMICAL
Aconaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrylonrtrile
Anthracene
Benzene
Benzole acid
Benzotrichloride
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Benzojg.h ,l)perytene
Benzo(k)fluoranthene
Bis(2-chloroethoxy) methane
Bis(2-chloroethyl)ether
Bls(2-chlorolsopropy))ether
B!s(2-ethylhexyl)phthalate
Bromodlchloiomethane
Bromoform
Bromomethane
Bromodlphenyl ether, p-
Butanone. 2- (Methyt ethyl ketone)
Butyl be nzylphthalate
Carbon disulflde
Carbon tetrachloiide
Chlordane
ChlofO-3-methylphenol, 4-
Chloroanillne, p- (4-Chloroaniline)
Chlorobenzene
Chlorobenzilate
Chtoroethane (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthalene, beta
Chlorophenol, 2-
Chlorodiphenyl ether, 4-
Chrysene
Cresol, m-
Cresol. o- (2-Methylphenol)
Cresol. p-
Crotonaldehyde
Cumene
DDE, 4.4'-
Diben*(a.h)anthraceno
Dibromochloromethane
Dichlorobenzene. 1.3-
Dichlorobenzene. 1.4-
Dichlorobenzene. 1.2-
Dichloroberuridme. 3.3'-
Dichlorobrphenyl
Inhalation
Slope
Factor
(mg/kg-d)"-1
NA
NF
77E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E»00
NF
NA
NA
2 7E-01
NA
8 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0 004375
NF
NA
0 04375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RfD
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
2 5E-02
1 4E-04
7 5E-02
4 3E-04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
5 OE 03
50E-03
5 OE-03
36E-04
NA
7 1E-02
50E 02
7 1E-04
1 4E-04
1 5E-05
NF
1 OE 03
1 4E-03
50E03
7 1E-01
25E-03
NA
20E 02
1 3E-03
NF
NA
1 3E-02
1 3E 02
1 3E-03
NA
64E-04
NA
NA
5 OE-03
NA
5 7E 02
1 4E 02
NA
MA
Emission
Rate
(g'sec)
67E 06
67E-06
3 OE-04
2 9E 03
2 9E 04
2 OE-04
55E-06
1 5E-05
'1 IE-OS
32E-05
55E-06
55E-06
55E-06
55E-06
55E-06
67E 06
1 3E 05
67E-06
37E OS
1 OE-04
55E-06
49EO4
6 7E 06
5 IE 05
55E 06
89E-05
1 6E 04
5 5E 07
67E 06
6 7E 06
55E06
3 7E 05
4 9E 04
2 7E 04
2 5E 04
67E 06
55E-06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
E1avg
E1 avg
El avg
El avg
El avg
E1 avg
E1 ivg
E1 avg
El »vg
El ivg
El avg
E1 avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
El avg
E1 avg
E1 avg
El avg
El avg
El avg
El avg
El avg
Et avg
E1 avg
; E 1 avg
El avg
E1 avg
E1 avg
E 1 avg
E 1 avg
E1 avg
E1 avg
El avg
E 1 avg
E 1 avg
Adult
Cancer
Risk
NT
NT
24E-11
NT
NT
49E-10
NT
44E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 5E-10
NT
NT
NT
22E 13
NT
NT
NT
NT
NT
BSE 11
73E-12
NT
NT
NT
10E-10
NT
22E-10
1 6E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
59E-11
NT
NT
1 2E-09
NT
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
3 7E-10
NT
NT
NT
54E-13
NT
NT
NT
NT
NT
2 IE 10
1 8E-11
NT
NT
NT
26E-10
NT
54E-10
39E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
NT
fjt
in
HI
(IT
NT
School age
Cancer
Risk
NT
NT
36E-11
NT
NT
74E-10
NT
66E-12
NT
NT
NT
NT
NT
NT
NT
NT
22E-10
NT
NT
NT
33E-13
NT
NT
NT
NT
NT
1 3E-10
1 1E-11
NT
NT
NT
1 5E-10
NT
33E-10
24E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
III
NT
NT
in
Farmer
Cancer
Risk
NT
NT
53E-11
NT
NT
1 1E-09
NT
97E-12
NT
NT
NT
NT
NT
NT
NT
NT
33E-10
NT
NT
NT
46E-13
NT
NT
NT
NT
NT
1 9E-10
16E-11
NT
NT
NT
23E-10
NT
49E-10
35E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
m
NT
tu
                                                                                                                                              Adult      Child   School age  Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HQ       HO
35E-08
NT
3 7E 05
92E 06
9 3E 07
1 1E 04
5 BE 09
27E-06
90E-10
NT
NT
NT
NT
NT
NT
NT
NT
53E-08
59E-07
1 6E-06
8 7E 08
1 1E-04
NT
5 7E 08
87E-09
99E-06
BSE 05
29E-06
NT
5 3E 07
3 IE 07
5 BE 07
5 4E 08
85E06
NT
2 7E 08
35E-07
NT
NT
3 5E 08
35E4J8
35E07
NT
6 BE 07
NT
m
4 2E 07
NT
7 RE 09
3 IE 08
in
in
1 3E-07
NT
1 4E 04
3 4E 05
35E06
42E 04
22E 08
1 OE 05
34E09
NT
NT
NT
NT
NT
NT
NT
NT
2 OE 07
22E06
61E06
33E07
4 1E-04
NT
2 IE 07
33E 08
3 7E 05
3 3E 04
1 IE-OS
NT
20E 06
1 IE 06
22E06
20E 07
32E 05
NT
99E 08
1 3EO6
NT
NT
1 3E 07
1 3E 07
1 3E 06
NT
2 5E 06
NT
NT
1 RF 06
NT
2 9f 08
1 IF 07
HI
Ml
8 OE-08
NT
84E 05
2 IE 05
2 IE 06
2 5E-04
1 3E 08
62E-06
20E-09
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-07
1 3E 06
37E06
2 OE 07
2 5E-04
NT
1 3E 07
20E 08
22E 05
2 OE 04
66E 06
NT
1 2E 06
69E07
1 3E 06
1 2E 07
1 9E 05
NT
60E 08
79E 07
NT
NT
79E 08
79E 08
79E 07
NT
1 5E 06
NT
NT
9 4E 07
MT
1 7E 08
6 IE 08
MT
MT
3 5E-08
NT
37E 05
92E 06
93E-07
1 IE 04
58E 09
2 7E 06
90E-10
NT
NTi
NT
NT
NT
NT
NT
NT
53E 08
59E07
1 6E 06
8 7E 08
1 1E-04
NT
5 7E 08
87E 09
99E 06
8 BE 05
29E 06
NT
53E 07
3 IE 07
5 BE 07
54E 08
85E 06
NT
2 7E 08
35E 07
NT
NT
35E 08
35E 08
35E 07
NT
6 BE 07
MT
NT
4 ?F 07
MT
7 RE 09
3 IF. 08
Mt
MT
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me V.
-------
TABLE 1  Average Inhalation Risks and Noncancer HQs in Subarea E1
CHEMICAL 1
Dichlorodifluoromelhane
Dichloroethane. 1,1- (Ethylidene dichloride)
Dichloroethane. 1,2-
Dichloroethene. 1.1- (Vinytidine chloride)
Dichloroethene (trans). 1.2-
Dtchlorophenol, 2,4-
Dichloropropane, 1 ,2- (Propylene dichloride)
Dichloropropene (cis). 1.3-
Dichloropropene (trans). 1 .3-
Diethylphthalate
Dimethoxybenzldine, 3,3'-
Dimethylphenol, 2.4
Dimethylphthalate
Di-n butytphthalate
Dinrtjololuene. 2.6-
Dinrtro-2-methylphenol, 4.6-
DinHrophenol. 2,4-
Dinrtrololuene. 2.4-
Dioxana, 1.4-
Di(n)octy) phthalate
D. 2,4-
Etnyt methacrylate
Ettiyibenzene
Ettiylene dibromide
Ethylene oxide
Ethylene thiourea
Fluoranthene
Fluorene
Formaldehyde
Furfural
Heptachlor
Heptachloroblphenyl
Hexachlorobenzene
Hexachlorobiphenyl
Hexachloiobutadlene
Hexachlorocyclohexane. gamma (LIndane)
Hexachlorocyclopentadiene
Hexachloroethane
Hexachlorophene
Hexanons. 2-
lndeno( 1 ,2 ,3-cd)pyrene
Isophorone
Maleic hydrazide
Methoxychlor
Methyl t-butyl ether
Methyl-2-Pentanone, 4- (MIBK)
Methylene chloride
Methylnaphlhalene. 2-
Monochlorobiphenyt
Naphthalene
Nitroanilme. 2-
tJ'ii inniline. 3-
Inhalation
Slope
Factor
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
7 BE -02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RfTJ
(mg/kg-d)
1 4E-02
36E-02
NA
2 3E 03
50E-03
7 5E-04
29EO4
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
25E-02
2 5E 04
NF
50E 04
50E04
NA
50E43
25E 03
23E 02
7 1E 02
1 4E-05
NA
20E 05
1 OE 02
1 OE-02
50E 02
36E-03
1 3E-04
NA
20E-04
NA
5 OE-05
75E-05
50E-06
2 5E 04
7 5E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 1E-01
NF
NA
1 OE-02
1 4E-05
NF
Emission
Rate
(g/sec)
2 5E 04
1 3E 05
1 3E-05
1 3E 05
1 3E 05
55E06
1 3E 05
' 1 3E-05
1 3E-05
1 7E 05
1 2E-04
S5E-06
55E06
1 6E 05
55E 06
55E06
55E06
55E06
4 9E 04
55E06
3 9E 05
25E 04
50E 04
1 2E 04
3 IE 05
1 5E 10
55E06
67E 08
6 IE 04
55E06
5 5E 07
1 4E 08
55E 06
1 4E 08
1 OE 04
55E05
55E 06
55E 06
3 2E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
El avg
E1 avg
E1 avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
El avg
E1 avg
El avg
E1avg
E1 avg
El avg
E1avg
El avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
Et avg
El avg
El avg
E1 avg
E1 avg
Et avg
El avg
El avg
El avg
El avg
Et avg
El avg
E1 avg
E1 avg
El avg
E1 avg
El avg
El avg
El avg
E1 avg
Et avg
El avg
El avg
E 1 avg
E t avg
E1 avg
El avg
El avg
E 1 avg
E 1 avg
E t avg
Adult
Cancel
Risk
NT
NT
1 2E 11
1 5E-10
NT
NT
NT
1 7E-11
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
89E 10
1 1E-10
NT
NT
NT
2BE-10
NT
25E-11
NT
90E-11
NT
80E-11
NT
NT
79E-13
NT
NT
NT
NT
NT
NT
NT
NT
6 7E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
29E 11
38E-10
NT
NT
NT
4 1E-11
4 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E 09
2 7E-10
NT
NT
NT
69E-10
NT
63E-11
NT
23E-10
NT
20E-10
NT
NT
20E 12
NT
NT
NT
NT
fIT
NT
ra
NT
1 7E-11
NT
NT
NT
NT
fa
School age
Cancer
Risk
NT
NT
1 7E 11
2 3E-10
NT
NT
NT
25E 11
25E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E-09
16E-10
NT
NT
NT
42E-10
NT
38E-11
NT
1 4E-10
NT
1 2E-10
NT
NT
1 2E-12
NT
NT
NT
NT
NT
ta
NT
NT
1 OF. 11
ta
NT
ia
UT
ta
Farmer
Cancel
Risk
NT
NT
26E-11
34E-10
NT
NT
NT
37E-11
37E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E-09
24E-10
NT
NT
NT
62E-10
NT
56E-11
NT
20E-10
NT
1 8E-10
NT
NT
1 7E-12
NT
NT
NT
NT
NT
fa
UT
NT
1 5F. 11
ta
ia
ta
ta
m
                                                                                                                                                Adult      Child   School age   Faimei
                                                                                                                                             Noncancer  Noncancet Noncancei  Noncancer
                                                                                                                                                HQ        HQ        HQ        HO
1 4E 06
28E-08
NT
4 4E 07
20E-07
5 BE 07
35E06
6 9E 07
69E 07
67E-09
NT
87E-OB
NT
50E-08
1 7E 06
NT
8 7E-07
87E-07
NT
87E4W
1 2E 06
86E^>7
55E 07
6 4E-04
NT
58E 10
44E 08
5 3E 08
9 6E 07
1 2E-07
35E-07
NT
22E-08
NT
16E-04
5 BE 05
87E-05
1 7E 06
34E-05
NT
NT
1 IE 08
7 3E 08
35E 08
46E 09
1 7E 07
1 SE 07
NT
NT
4 4E 08
1 7F OS
tit
51E 06
1 OE 07
NT
1 6E 06
7 4E 07
22E 06
1 3E 05
26E 06
26E 06
2 5E 08
NT
3 3E-07
NT
1 9E 07
65E-06
NT
33E-06
33E-06
NT
3 3E 07
46E06
32E 06
2 1E 06
2 4E 03
NT
22E 09
1 6E 07
20E 07
36E 06
4 6E 07
1 3E 06
NT
82E-06
NT
60E 04
22E 04
33E 04
65E 06
1 3E 04
NT
NT
40E 08
2 7E 07
1 3E 07
1 7F 08
65F 07
sr,r o?
m
NT
1 r,[ 07
1 4f M
III
3 1E 06
6 3E-08
NT
1 OE 06
45E 07
1 3E 06
7 BE 06
1 6E 06
16E06
1 5E-08
NT
20E-07
NT
1 IE 07
39E-06
NT
20E06
20E-06
NT
2 OE-07
2 BE 06
20E06
1 3E 06
1 4E 03
NT
1 3E 09
99E08
1 2E 07
22E06
2 BE 07
7 9E-07
NT
49E06
NT
36E 04
1 3E 04
20E 04
39E 06
7 7E 05
NT
NT
24E 08
1 6E 07
79E 08
1 OE 08
39E 07
3 IF 07
NT
NT
99E 08
B 4F. m
NT
1 4E 06
2 BE -08
NT
4 4E 07
20E 07
58E 07
35E06
69E07
69E 07
67E-O9
NT
8 7E-08
NT
5 OE OB
1 7E-06
NT
B 7E 07
87E-07
NT
8 7E 08
1 2E 06
B6E C7
55E 07
6 4E-04
NT
5 BE 10
44E 08
5 3E 08
96E07
1 2E 07
35E-07
NT
22E06
NT
1 6E 04
5 BE 05
87E05
1 7E 06
34E05
NT
NT
1 1E OB
73E08
35E 08
46E 09
1 7E 07
1 5E 07
NT
NT
44E 08
3 7E 05
fIT
-------
  TABLE 1  Average Inhalation Risks and Noncancel HQs in Subarca E 1
  CHEMICAL

  Nifroaniline. 4-
  Nihobenzene
  Nilrophenol. 2-
  Nrtrophenol, 4-
  N Nrtroso-di-n butytimine
  N-Nitroso-dl-n-propytamlne
  N Nrtrosodiphenylamine (Diphenylamine)
  Nonachloroblphenyl
  Octachloroblphenyi
  Pentschlorobenzene
  Pentachloroblpbenyt
  PentachloronMrobenzene
  P«ntachloroph«nol
  Phenanthrene
  Phenol
  Pytene
  Safrole (5-(2-Propeny1). 1,3-benzodioxole)
  Styrene
  Tetoachlorobiphenyl
  Tetrachtoroelhane. 1,1.1 2
 Tetrachloroelhane. 1.1.2.2
 Tetrachloroethene
 Tetrachlorophenol. 2,3,4.6
 Toluene
 Tr1chloro-1,2.2-trifluoroethane. 1.1.2-
 Trichlorobenzene, 1,2.4-
 Trichloroblphenyl
 Trichloroethane, 1,1.1- (Methyl chloroform)
 Trichloroethane. 1,1,2-
 Trlchloroethene
 Trichlofofluoromethane
 TfichlorophencH. 2.4.5-
 Trichloropheno). 2,4.6-
 Vlnyl acetate
 Vinyl chloride
 Xylene. m/p- (m/p-Dtmethyl benzene)
 Xylene, o- (o-Dimethyl benzene)
Inhalation
Slope
Factor
(mg/kg-d)A-
NF
NA
NF
NF
54E*00
NA
Kla\
NA
(.1*
NA
K1A
NA
*.i*
NA
NA
NA
» i*
NA
NA
NA
NF
NA
NA
26E-02
2 OE-01
20E 03
NA
NA
NA
NA
NA
NA
5 7E-02
6 OE-03
NA
NA
1 OE-02
NA
3 OE-01
NA
NA
RAC
1 (mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
0 02625
NF
0 25
NA
0 02625
NA
000875
0 02625
0 t
7 5
005
NA
025
00035
NA
0 175
00875
NA
DOS
NA
1 75
1 75
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
. NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
15E-01
7 5E-03
NF
7 1E-02
NA
75E 03
NA
2 5E 03
75E03
29E 02
2 1E»00
1 4E-02
NA
7 IE 02
1 OE-03
NA
5 OE 02
2 5E-02
NA
1 4E-02
NA
5 OE-01
5 OE-01
Emission
Rate
(g/sec)
67E-06
55E06
67E 06
55E06
12E-04
67E-06
6 7E-06
1 4E-08
' 1 4E-08
48E-05
1 4E-08
34E-05
55E-06
67E-08
55E06
55E-06
1 2E 04
23E-05
1 4E 08
55E06
55E 06
5 IE-OS
6 BE 4)6
6 1E44
33E 04
55E 06
30E 08
1 3E4>5
1 3E 05
t 9E 05
25E04
55E 06
55E-06
6 4E-05
25E 04
38E 04
55E-06
Subarea
El avg
E1 avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
El avg
Et avg
El avg
Et avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
Oftsile
Vapor
Cone
(ug/m3)
1 9E 06
6E 06
9E-06
6E06
5E 05
9E 06
9E 06
1E-09
1E-09
4E-05
1E-09
8E-06
6E06
9E06
1 6E 06
1 6E 06
33E4)5
65E06
4 IE 09
1 6E 06
1 6E 06
1 5E-05
20E-06
1 BE 04
9 6E 05
1 6E 06
8 BE 09
36E-06
36E 06
54E-06
7 IE-OS
6E-06
6E-06
9E 05
IE 05
IE 04
6E-06
Cancer
Adult
Dose
(mg/kg-d)
68E-11
56E-11
68E-11
56E-11
1 2E-09
68E 11
68E-11
1 4E-13
1 4E-13
49E-10
1 4E-13
34E-10
56E-11
66E-11
56E-11
56E-11
1 2E-09
23E-10
1 4E-13
56E 11
56E-11
52E-10
69P-11
63E 09
34E-09
56E-11
3 1E-13
t 3E-10
1 3E-10
1 9E-10
25E-09
56E-11
56E-11
66E-10
25E-09
39E-09
56E-11
Cancer
Child
Dose
(mg/kg-d)
1 7E-10
1 4E 10
1 7E-10
1 4E 10
3 1E-09
1 7E-IO
1 7E 10
36E-13
36E-13
1 2E-09
36E-13
86E-10
1 4E-10
1 7E-10
1 4E-10
1 4E-10
29E-09
57E-10
36E-13
1 4E-10
1 4E-10
1 3E-09
1 7E 10
16E-08
84E09
1 4E-10
77E-13
32E-10
32E 10
47E-10
62E-09
1 4E-10
14E-10
1 6E-09
62E-09
97E-09
1 4E-10
Cancer
School age
Dose
(mg/kg d)
1 OE-10
BSE 11
1 OE-10
85E-11
1 9E 09
t OE 10
IDE 10
22E 13
22E 13
73E-10
22E-13
52E-10
85E-11
1 OE-10
85E-11
BSE 11
1 BE -09
35E-10
22E-13
85E-11
BSE 11
79E-10
10E 10
94E-09
51E-09
85E 11
46E-13
1 9E-10
1 9E-10
29E-10
3 BE -09
85E-11
65E-11
99E-10
3 6E-09
5 8E 09
85E-11
Cancer
Farmer
Dose
(mg/kg-d)
1 5E 10
1 2E 10
1 5E 10
1 2E 10
2 7E 09
1 5E 10
1 5E-10
32E-13
32E 13
1 1E-09
32E 13
76E-10
1 2E-10
1 5E-10
1 2E-10
1 2E 10
26E09
51E-10
32E 13
2E 10
2E-10
2E09
5E 10
4E 08
75E09
12E 10
69E 13
2 BE 10
2 BE 10
42E 10
56E09
1 2E 10
1 2E-10
15E09
5 6E-09
8 6E 09
1 2E-10
Noncancer
Adult
Dose
(mg/kg-d)
53E-10
44E 10
53E 10
44E 10
96E 09
53E-10
53E 10
1 IE 12
1 1E-12
3 BE 09
1 1E-12
27E-09
44E-10
53E 10
44E 10
44E 10
9 IE 09
1 BE 09
1 IE 12
44E 10
44E 10
4 IE 09
54E-10
49EOB
26E 08
44E 10
24E 12
99E 10
99E 10
1 5E 09
1 9E 08
44E-10
44E-10
51E-09
1 9E-08
30E-08
44E-10
Noncancer
Child
Dose
(mg/kg-d)
20E 09
1 6E 09
20E 09
16E-09
36E08
2 OE 09
20E-09
42E 12
42E-12
1 4E-08
42E 12
IDE -08
16E-09
20E09
1 6E-09
1 6E-09
3 4E 08
67E 09
42E-12
16E-09
16E4M
1 5E 08
20E-09
1 BE 07
9 BE 08
16E-09
90E 12
3 7E-09
37E 09
55E 09
73E 08
1 6E 09
1 6E 09
1 9E 08
7 3E 08

16E 09
Noncancer
School age
Dose
(mg/kg-d)
1 2E 09
99E 10
1 2E 09
99E 10
2 2E-08
1 2E 09
1 2E-09
25E-12
25E-12
85E-09
25E-12
60E-09
99E-10
1 2E4»
99E-10
99E 10
2 1E 08
40E-09
25E-12
99E-10
99E-10
92EO9
1 2E 09
1 1EX)7
S9E 08
99E 10
54E 12
22E-09

33E-09
4 4E-08
99E-10
99E 10
1 2E 08
44E 08
6 BE 08
99E 10
Noncancer
Farmer
Dose
(mg/kg-d)
53E 10
44E-10
53E 10
44E-10
96E-09
53E 10
53E 10
1 1E-12
1 1E 12
3 BE -09
r 1 IE 12
"27E4J9
44E 10
53E 10
44E-10
44E-10
9 IE 09
1 BE 09
1 1E-12
44E 10
44E 10
4 1E4W
54E 10
4 9E-OB
26E 08
44E 10
24E-12
99E 10
99E-10
1 5E-09
1 9E-08
44E-10
44E 10
5 1E-09
1 9E 08
30E-08
44E 10
 2.3.7.8-TCDD
 1.2,3.7.8 PCDD
 1.23.4,7.PHxCDD
 1.23.67.e HxCDD
 1.2.3.7.8.9 HxCDD
 1,2.3.4.6.7.8 HpCDD
 OCDD
 2.3.7.8 TCDF
 1.2.3.7.8PCDF
 2.34 7.8PCDF
 1.2 34.78 HxCDF
 1.2 3 6 7 8 HxCDF
 2.34.6.7.8 HxCDF
15E+05
75E»04
1 5E»04
1 5E»04
1 5E+04
1 5E«03
1 5E«02
1 5E»04
75E+03
75E*04
1 5E«04
1 5E»04
1 5E+04
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
flA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
HA
1 08E-11
678E-11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
E1 avg
E1 avg
El avg
E1 avg
61 avg
E 1 avg
E 1 avg
E 1 avg
E 1 avg
E t avg
El avg
E 1 avg
E 1 avg
3 IE 12
20E 11
26E 11
4 BE 11
32E 11
36E 10
1 BE 09
25E tl
1 OE to
1 4E 10
4 1E to
39E 10
4 4E to
1 IE 16
69E 16
9 1E-16
1 7E 15
i IE 15
1 3E 14
63E 14
90E 16
35E 15
48E 15
1 5E 14
1 4E 14
1 5E 14
2 7E 16
1 7E 15
23E 15
4 2E 15
28E 15
32E 14
1 6E 13
2 2E 15
88E 15
1 2E 14
36E 14
34E 14
38F 14
1 7E 16
1 OE 15
1 4E 15
25E 15
1 7E 15
1 9E 14
94E 14
1 3E 15
5 3E 15
72E 15
2 ?E 14
2 IE 14
2 IE 14
25E 16
1 5E-15
20E 15
3 BE 15
25E 15
2 BE 14
t 4E 13
2 OF 15
7 BE 15
1 IE 14
3 ?r 14
3 Of 14
1 4f 14
86E-16
54E 15
7 IE 15
1 3E 14
86E 15
99E 14
49E 13
70E 15
2 7E 14
3 7E 14
1 IE 13
1 IE 13
1 ?F 11
32E 15
20E 14
2 7E 14
49E 14
32E 14
3 7E 13
1 BE 12
2 BE 14
1 OE 13
1 4E 13
4 2E 13
4 OE 13
4 •iF 11
1 9E 15
1 2E 14
1 6E 14
30E 14
20E-14
22E 13
1 IE 12
1 6E 14
62E 14
84E 14
26E 13
24E 13
2 7F 11
B6E 16
54E 15
7 IE 15
1 3E 14
86E 15
99E 14
49E 13
70E 15
2 7E 14
3 7E 14
1 IE 13
1 IE 11
1 2F 11
Volume V. Appendix7
-------
TABLE 1  Average lriv   /jn Risks and Noncancer HQs in Subarea E1
CHEMICAL
Nrtroaniline, 4-
Nitiobenzene
Nit/ophenol, 2-
Nrtiophenol, 4-
N Nilioso di n butylamine
N Nrtroso-dl n piopylamine
N-Nrtrosodiphenylamlne (Diphenylamlne)
Nonachlorobiphenyl
Octachloroblphenyi
Pentachlorobenzene
Pentachlorobiphenyl
Pantachloronitrobenzene
Pentachlor ophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl)- 1 ,3-benzodioxole)
Styrene
Tetrachlorobiphenyl
Tetrachloroethane. 1.1.1.2-
Tetrachloroethane. 1.1,2.2-
Tetrachloroethene
Tetrachlorophenol. 2,3,4.6-
Toluene
Trlchloro-1 .2.2-tnfluoroelhane. 1.1 .2-
Trichloroberizene, 1.2.4-
Trlchlorobiphenyl
Trichtoroethane. 1.1 .1- (Methyl chloroform)
Trichloroethane. 1,1.2-
Trichloroethene
Tricolor ofluoromethane
Trichlorophenol. 2,4,5-
Trichlorophenol, 2,4.6-
Vinyt acetate
Vinyl chloride
Xylene, m/p- (m/p-Dimethyl benzene)
Xylene, o- (o-Dimettiyl benzene)
2,3,7.8-TCDD
.2.3.7.8PCDD
.2,3.4.7.8 HxCDD
,2, 3 6, 7 8 HxCDD
.2.3.7.8.9 HxCDD
,2,3.4,6.7,8-HpCDD
OCDD
2.3.7.8-TCDF
1.2. 3 7.8 PCDF
2.3 4.7.8 PCDF
1 2 34.78HxCDF
1 2.36.78HxCDF
2,3 4.6.7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)"- 1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E 02
20E 01
20E 03
NA
NA
NA
NA
NA
NA
5 7E 02
6 OE-03
NA
NA
1 OE-02
NA
3 OE 01
NA
NA
1 5E*05
7 5E+04
5E+04
5E+04
5E»04
5E+03
5E*02
5E»04
75E»03
75E+04
1 5E«04
1 5E»04
1 5E«04
RAC
(mg/m3)
NF
00005
NF ..
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
002625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E04
7 5E-03
NA
1 5E 01
7 5E-03
NF
7 1E 02
NA
7 5E-03
NA
25E 03
7 5E 03
2 9E 02
2 1E«00
1 4E-02
NA
7 1E 02
1 OE-03
NA
50E 02
2 5E-02
NA
1 4E-02
NA
50E-01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E 06
55E 06
6 7E 06
55E 06
1 2E-04
67E 06
6 7E 06
1 4E-08
1 4E^>8
48E05
1 4E-08
34E-05
55E-08
6 7E-08
55E-06
55E 06
1 2E 04
23E-05
1 4E 08
55E 06
55E 06
5 IE-OS
68E06
6 1E 04
3 3E 04
55E 06
30E08
1 3E-05
1 3E-05
1 9E-05
25E-04
55E06
55E-06
6 4E-05
2 5E 04
3 BE -04
55E-06
1 08E-11
6 78E-11
895E 11
1 66E 10
1 09E-10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
El avg
E1 avg
E1 avg
El avg
E1 avg
Et avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
El avg
El avg
E1 avg
E1 avg
El avg
El avg
E1 avg
E1 avg
E1 avg
El avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
Et avg
El avg
Et avg
El avg
El avg
E 1 avg
E1 avg
E 1 avg
E 1 avg
E 1 avg
E 1 avg
El avg
E 1 avg
El avg
F. 1 avg
Adult
Cancer
Risk
NT
NT
NT
NT
6 7E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E-12
1 IE 11
1 1E-12
NT
NT
NT
NT
NT
NT
73E-12
1 1E-12
NT
NT
56E-13
NT
75E-10
NT
NT
1 7E 11
52E 11
1 4E-1I
25E 11
1 7E 11
1 9E-11
94E 12
1 3E 11
26E 11
36E 10
2 2E 10
20E 10
2 3E 10
Child
Cancer
Risk
NT
NT
NT
NT
1 7E 08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E 12
28E 11
26E-12
NT
NT
NT
NT
NT
NT
1 BE 11
2BE-12
NT
NT
1 4E-12
NT
1 9E-09
NT
NT
4 IE 11
1 3E 10
34E 11
6 3E 11
42E 11
4 7E 11
2 3E 11
3 3E 11
66E 11
89E 10
54E 10
5 IE 10
5 7E 10
School-age
Cancer
Risk
NT
NT
NT
NT
1 OE-O8
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E-12
1 7E-11
1 6E-12
NT
NT
NT
NT
NT
NT
1 TE-11
1 7E-12
NT
NT
85E-13
NT
1 IE-OS
NT
NT
25E-11
76E 11
2 IE 11
3 BE 11
2 5E 11
29E 11
1 4E 11
20E 11
40E 11
5 4E 10
3 3E 10
3 IE 10
35E 10
Farmer
Cancer
Risk
NT
NT
NT
NT
1 5E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
32E-12
25E-11
24E-12
NT
NT
NT
NT
NT
NT
16E-11
25E-12
NT
NT
1 2E-12
NT
1 7E-09
NT
NT
37E 11
1 2E 10
30E 11
56E 11
3 7E 11
4 2E 11
2 1E 11
30E 11
59E 11
79E 10
49E 10
4 5E 10
5 1E 10
                                                                                                                                              Adult      Child   School age   Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ       HO       HQ       HQ
NT
3 1E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E-06
5 BE -08
NT
29E-09
5 BE -08
NT
25E-08
NT
5 8E-08
NT
1 6E 06
72E 08
1 7E-06
1 2E-08
3 1E-08
NT
1 4E 08
9 9E-07
NT
3 9E-07
1 7E-08
NT
36E-07
NT
60E-08
87E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
(IT
U!
NT
1 1E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 05
22E-07
NT
1 IE 08
2 2E-07
NT
93E-08
NT
22E-07
NT
61E46
27E^)7
64E06
•I6E-08
1 IE 07
NT
52E08
37E06
NT
1 5E 06
6 5E 08
NT
1 3E-06
NT
23E 07
33E09
NT
NT
NT
NT
NT
HI
HI
tJT
111
III
HI
NT
Ml
NT
69E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
81E-03
1 3E-07
NT
66E09
1 3E-07
NT
5 6E-08
NT
1 3E-07
NT
37E 06
1 6E 07
38E06
2 BE 08
6 9E 08
NT
3 IE 08
22E 06
NT
8 BE 07
39E 08
NT
8 IE 07
NT
t 4E 07
20E 09
NT
NT
HI
m
NT
(IT
NT,
NT
FIT
NT
(IT
NT
m
NT
3 1E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E 06
5 BE -08
NT
29E-09
5BE-08
NT
25E-08
NT
58E4M
NT
16E 06
72E08
1 7E 06
1 2E 08
31E 08
NT
1 4E 08
99E 07
NT
39E 07
1 7E 08
NT
36E07
NT
6 OE 08
87E 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
        V. Appendix V-14
-------
TABLE 1  Average Inhalation Risks and Noncancof HQs in St/baiea E 1
CHEMICAL
12378 9 HxCDF
1 2.3.4.6, 7.8-HpCDF
1.2,3.4. 7,8.9 HpCDF
OCDF
Dioxtn TEQ
Muminum
Antimony
Msenic
Barium
3erytlium
Cadmium
Chromium (hexavaleni)
Chromium (bivalent)
Copper
ead
Mercury (and MeHg)
Jtckel
Selenium
5ilvet
Thallium
^inc
hydrogen chloride
otal nibogan oxides (NOx)
Total sulfur oxides (SOx)
'articulate matter
}e«pirable participates
Inhalation
Slope
Factor
(mg/kg d)«-1
1 5E*04
1 5E*03
1 5E+03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000)25
0 004375
0000438
0004375
0875
NA
NA
0000075
00175
0 004375
0004375
0000061
02625
OOO175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E-05
36E 05
1 3E 03
1 3E 04
1 3E 03
2 5E-01
NA
NA
2 1E 05
50E 03
1 3E 03
1 3E 03
1 8E 05
75E 02
50E-04
NA
NA
NA
NF
Emission
Rate
(g'sec)
293E-10
930E-09
1 22E-09
1 89E 08
4 28E 08
2 4E 04
4 2E-06
37E05
1 5E^)4
33E-08
1 6E-05
7 1E-07
7 1E^)7
94E-05
43E05
1 4E 03
50E-06
4 7E 04
15E05
34E-05
1 2E-04
3 2E-02
24E*00
9 1E-02
7 2E 02
72E-02
Subarea
El avg
El avg
El avg
El avg

Et avg
El avg
El avg
El avg
Eltvg
Et avg
El avg
E1 avg
Et avg
El avg
El avg
El avg
El avg
E1 avg
El avg
Et ivg
El avg
Et avg
E1 avg
Et avg
E1 avg
Oft site
Vapor
Cone
(ug/m3)
85E-11
2 7E-09
35E 10
5 5E 09
1 2E-08
70E05
12E-06
1 IE 05
44E 05
96E 09
46E06
21E07
2 1E-07
27E 05
1 2E 05
4 1E 04
1 5E 06
1 4E-04
44E 06
99E46
35E 05
93E 03
7 OE 01
26E 02
2 IE 02
2 1E 02
Cancer
Adult
Dose
(mg/kg d)
30E-15
95E 14
t 2E 14
1 9E-13
44E 13
2 5E-09
43E-1t
38E-10
1 5E 09
34E 13
1 6E-10
72E-12
72E-12
96E 10
44E-10
1 4E 08
5 1E-11
48E-09
1 5E-10
35E 10
1 2E 09
33E-07
25E-05
9 3E 07
74E-07
74E-07
Cancer
Child
Dose
(mg/kg-d)
75E-15
24E 13
3 IE 14
48E-13
1 IE 12
6 IE 09
1 1E-10
94E 10
38E 09
84E 13
4 1E-10
1 8E-11
1 8E-11
24E 09
1 1E-09
3 6E 08
1 3E-10
1 2E-08
36E 10
86E 10
3 1E 09
8 1E-07
62E 05
23E06
1 8E 06
1 8E 06
Cancer
School age
Dose
(mg/kg d)
4 5E-15
1 4E-13
1 9E-14
29E-13
66E-13
37E-09
65E-11
57E-10
23E 09
5 IE 13
25E-10
1 1E-11
1 1E-11
1 4E-09
66E-10
22E 08
7 7E 11
72E-09
2 3E-10
52E-10
1 BE -09
4 9E-07
3 7E-05
14E-06
t IE 06
1 IE 06
Cancer
Farmer
Dose
(mg/kg d)
66E 15
2 IE 13
2 BE 14
43E 13
97E 13
54E09
95E-11
84E tO
3 4E-09
75E 13
36E-10
16E-11
t 6E-11
2 1E-09
98E-10
32E08
1 1E-10
1 IE 08
34E-10
77E 10
2 7E-09
73E-07
55E05
2 IE 06
t 6E 06
1 6E-06
Noncancer
AduH
Dose
(mg/kg.d)
2 3E-14
74E-13
97E 14
15E 12
34E-12
19E-08
33E-10
29E 09
1 2E-08
26E 12
1 3E-09
56E 11
56E-11
75E09
34E-09
1 IE 07
40E 10
37E^)8
1 2E 09
27E^»
95E-09
25E^»
19E 04
72E06
57E06
57E 06
Noncancer
Child
Dose
(mg/kg-d)
8 7E-14
2 BE 12
36E 13
56E 12
1 3E 11
7 IE-OB
1 2E 09
1 IE 08
45E 08
9BE-12
47E09
2 IE 10
2 1E-10
2 BE -08
1 3E 08
4 2E 07
1 5E-09
1 4E-07
45E-09
10E-08
36E 08
95E-06
72E4M
2 7E05
2 1E^5
2 IE 05
Noncancer
School-age
Dose
(mg/kg-d)
53E-14
1 7E-12
22E 13
34E-12
77E 12
4 3E-08
75E 10
66E09
2 7E-08
59E-12
29E09
1 3E 10
t 3E-10
1 7E-08
77E-09
2 5E-07
90E-10
84E 08
27E-09
6 IE 09
2 2E-08
57E 06
4 3E 04
1 6E 05
1 3E-05
1 3E 05
Noncancer
Farmer
Dose
(mg/kg d)
2 3E-14
74E 13
97E 14
1 5E 12
34E-12
1 9E-08
33E 10
2 9E 09
1 2E-08
26E-12
1 3E-09
5 BE 11
56E-11
75E 09
34E 09
1 IE 07
40E 10
3 7E 08
12E09
27E09
95E 09
25E-06
1 9E 04
72E 06
57E06
5 7E-06
JOTES
  NA - Not applicable
  NF = Not found       ^
  NT * No toxicrty information
  HQ = Hazard quotient
  HI •= Hazard Index
 olume V. Appendix V-.'-
-------
TABLE 1  Average Inn,,—..on Risks and Noncancer HQs in Subarea E 1
CHEMICAL
1.2.3. 7.8.9 HxCDF
1. 2.3.4.6.7.8 HpCDF
1.2.3.4. 7.8.9 -HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsenic
Barium
Ben/Ilium
Cadmium
Chromium (hexavalent)
Chromium (divalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Resplrable particulars
Inhalation
Slope
Factor
(mg/kg-d)"-1
1 5E+04
1 5E+03
1 5E»03
1 5E»02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000436
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E-05
36E-05
1 3E 03
13E^)4
1 3E-03
25E-01
NA
NA
2 1E^>5
50E^)3
1 3E-03
1 3E 03
1 BE 05
7 5E-02
5 OF 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E 10
9 30E 09
1 22E 09
1 89E 08
4 28E 08
24E04
42E06
37E-05
1 5E 04
33E 08
1 6E-05
7 1E-07
7 1E-07
94E-05
43E 05
1 4E 03
50E 06
47E-04
1 5E 05
34E05
1 2E-04
3 2E-02
24E»00
9 IE 02
7 2E 02
7 2E 02
Subarea
El avg
El avg
El avg
El avg

E1 avg
El avg
El avg
El avg
El avg
E1 avg
El avg
E1 avg
El avg
E1 avg
El avg
El avg
El avg
El avg
El avg
E1 avg
E1avg
El avg
El avg
E1 avg
El avg
Adult
Cancer
Risk
45E-11
1 4E 10
1 9E 11
29E 11
1 4E-09
NT
NT
1 9E-08
NT
28E-12
1 OE-09
30E-10
NT
NT
NT
NT
43E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
1 1E-10
35E 10
47E-11
72E-11
3 6E 09
NT
NT
4 7E-08
NT
7 1E-12
25E-09
74E-10
NT
NT
NT
NT
1 1E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
68E-11
2 1E-10
28E-11
44E 11
2 2E 09
NT
NT
2 BE -08
NT
43E-12
1 5E 09
45E-10
NT
NT
NT
NT
65E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
1 OE-10
32E 10
42E-11
64E 11
32E-09
NT
NT
4 2E-08
NT
63E-12
2 2E-09
66E-10
NT
NT
NT
NT
95E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Adult
Noncancer
HQ
NT
NT
NT
NT
NT
NT
33E-06
39E-05
33E^)4
2 1E-09
10E-05
4 5E-08
23E-10
NT
NT
52E-03
79E-08
30E-05
95U-07
15E-04
13E-07
5 IE-OS
NT
NT
NT
NT
Child
Noncancer
HQ
NT
NT
NT
NT
NT
NT
1 2E 05
1 5E 04
1 2E 03
78E09
38E-05
1 7E-07
84E-10
NT
NT
19E42
3 OE 07
1 1E-04
36E4)6
5 8E O4
47E^)7
19E-02
NT
NT
NT
NT
School age
Noncancer
HQ
NT
NT
NT
NT
NT
NT
75E 06
8 BE 05
7 5E 04
47E 09
23E05
10E-07
51E-10
NT
NT
1 2E 02
1 8E-07
67E-05
22E46
35E04
29E-07
1 ^E-02
NT
NT
NT
NT
Farmer
Noncancer
HQ
NT
NT
NT
NT
NT
NT
33E06
3 9E 05
3 3E 04
2 1E 09
10E05
4 5E 08
23E-10
NT
NT
5 2E-03
7 9E 08
30E 05
9 5E 07
1 5E 04
1 3E-07
5 1E-03
NT
NT
NT
NT
                                                                                Total Risk    32E-08    7 9E-08    4 8E-08   7 IE 08
                                                                                                                                     Total HI    1 2E-02
                                                                                                                                                                   2 8E 02   1 2E 02
NOTES
  NA « Not applicable
  NF « Not found       ";
  NT * No loxlcrty information
  HQ * Hazard quotient
  HI  * Hazard Index
 'olume V. Appendix V-14
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TABL E 2 Average Inhalation Risks and Noncancei HQs in Subarea E 2
                                                                                                                                                                                   V    J
CHEMICAL
Acenaphthene
Acenaphthylene
Acelaldehyde
Acetone
Acelophenone
Acrylonttrile
Anthracene
Benzene
Benzole acid
Benzotrichlorki*
Benzo(a)anthticene
Benzo(a)pyren»
Benzo(b)fluorinlhene
Benzo(g,h,f)perylene
Benzo(k)fluoranthene
Bls(2-chloroethoxy) methane
Bis(2 -chloroethyl)ether
Bls(2-chlorolsopropyl)ether
Bis(2-ethylheKyl)phthalate
Bromodichloromethane
Bromoform
Bromomelhane
Bromodiphenyt ethef . p-
Bi/tanone. 2- (Methyl ethyt ketons)
Butylbenzytphtha'.ate
Carbon disulfide
Carbon tetrachlorlde
Chlotdane
Chtoro-3-melhytphenol. 4-
Chlotoaniline, p- (4-Chloroanihne)
Chlorobenzene
Chlotobenzilate
Chloroethane (Ethyl chloride)
Chloroform
Chlotomethane
Chloronaphthalene. beta
Chlorophenol, 2- -:
Chlorodiphenyl ether, 4-
Chrysene
Cresol, m-
Cresol. o- (2-Methylphenol)
Cresol. p-
Crotonaldehyde
Cumene
DDE. 4,4 -
Dibenz(a,h)anthtacene
Dibromochlotomelhane
Dichlorobenzene. 1.3-
Dichlorobenzene. 1 4-
Dichlorobenrene, 1.2-
Dichlotobenzidme, 3.3'-
Oichlofobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)A-1
NA
NF
7 7E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E 03
NA
NA
NA
NA
NA
53E 02
1 3E+00
NF
NA
NA
2 7E-01
NA
8 1E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
6 4E 04
2 5E 02
2 5E 02
1 4E 04
75E 02
43E-04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E03
50E 03
50E 03
36E-04
NA
7 1E 02
50E 02
7 1E 04
1 4E 04
1 5E-05
NF
1 OE-03
1 4E 03
50E 03
7 1E-01
2 5E-03
NA
2 OE 02
1 3E-03
NF
NA
1 3E-02
1 3E-02
1 3E 03
NA
64E-04
NA
NA
5 OE-03
NA
57E 02
1 4E 02
NA
NA
Emission
Rate
(g'sec)
6 7E-06
6 7E 06
30E 04
2 9E 03
29E 04
2 OE 04
55E-06
t 5E-05
1 IE-OS
32E-05
55E-06
55E06
55E-06
55E-06
55E 06
67E06
1 3E 05
67E-06
37E-05
1 OE 04
55E^)6
49E 04
67E-06
5 1E-05
55E 06
89E^»
1 6E-04
55E-07
67E-06
67E-06
55E-06
3 7E-05
4 9E-04
2 7E-04
2 5E 04
6 7E-06
55E 06
67E 06
55E-06
55E 06
55E 06
55E-06
1 4E 04
55E 06
55E-07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2ivg
E2avg
E2»vg
E2*vg
E2 avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2tvg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2 avg
E2avg
E2avg
E2 avg
E2 avg
E2 avg
E2avg
E2 avg
E2 avg
E2 avg
E2avg
E2avg
E2 avg
E2 avg
Adult
Cancer
Risk
NT
NT
1 1E-11
NT
NT
24E-10
NT
2 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
72E-11
NT
NT
NT
1 OE-13
NT
NT
NT
NT
NT
4 1E-11
35E-12
NT
NT
NT
50E-11
NT
1 1E-10
76E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HT
NT
NT
Child
Cancer
Risk
NT
NT
28E 11
NT
NT
59E-10
NT
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
NT
NT
NT
26E-13
NT
NT
NT
NT
NT
1 OE-10
87E-12
NT
NT
NT
1 2E-10
NT
26E-10
1 9E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
HI
IJT
HT
NT
NT
School age
Cancel
Risk
NT
NT
1 7E-11
NT
NT
36E-10
NT
32E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
1 6E-13
NT
NT
NT
NT
NT
62E 11
53E 12
NT
NT
NT
75E-11
NT
1 6E-10
1 1E-11
NT
NT
NT
NT
NT
NT
NT
tJT
NT
m
in
in
tn
NT
NT
HI
NT
Faimer
Cancer
Risk
NT
NT
25E-11
NT
NT
53E-10
NT
4 7E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
23E-13
NT
NT
NT
NT
NT
9 IE 11
78E-12
NT
NT
NT
1 1E-10
NT
23E 10
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
m
tn
NT
IIT
IIT
NT
NT
IIT
tn
                                                                                                                                                Adult      Child   School age   Farmer
                                                                                                                                              Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                 HQ       HQ       HQ        HO
1 7E-08
NT
1 8E-05
44E 06
45E07
5 4E 05
2 8E-09
t 3E-06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 6E-08
2 9E-07
7 9E 07
4 2E 08
53E-05
NT
2 BE 08
4 2E 09
48E 06
4 2E 05
1 4E-06
NT
2 6E-07
1 5E 07
2 8E 07
2 6E 08
41E-06
NT
1 3E 08
1 7E-07
NT
NT
1 7E 08
1 7E 08
1 7E-07
NT
3 3E 07
NT
NT
2 OF 07
NT
3 7E 09
t 5E 08
IIT
tn
64E 08
NT
6 7E 05
1 7E 05
1 7E 06
2 OE 04
1 IE 08
49E06
1 6E-09
NT
NT
NT
NT
NT
NT
NT
NT
9 6E 08
1 1E 06
30E06
1 6E 07
2 OE 04
NT
1 OE 07
1 6E 08
1 BE 05
1 6E-04
53E 06
NT
9 6E 07
55E 07
1 IE 06
9 8E 08
15E05
NT
48E 08
6 3E 07
NT
NT
63E 08
63E 08
63E 07
NT
1 ?F. 06
tn
NT
7 r,F 07
NT
1 F 08
IIT
m
3 9E-08
NT
4 IE 05
1 OE 05
1 OE 06
1 2E 04
63E 09
30E-06
98E-10
NT
NT
NT
NT
NT
NT
NT
NT
5 BE 08
64E-07
18E06
9 5E 08
1 2E-04
NT
62E-08
95E-09
1 1E 05
96E 05
326-06
NT
58E 07
33E 07
64E07
59E08
92E 06
NT
29E 08
38E 07
NT
NT
3 BE 08
3 BE 08
3 BE 07
NT
7 4F. 07
fW
NT
4 6F. 07
NT
83E 09
3 IF 08
NT
flT
1 7E 08
NT
1 BE 05
4 4E 06
45E07
5 4E 05
2 BE 09
t 3E 06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 6E-08
2 9E 07
79E 07
42E08
53E 05
NT
2 BE 08
42E 09
4 BE 06
42E 05
1 4E 06
NT
26E 07
1 5E 07
2 BE 07
26E 08
4 1E-06
NT
1 3E 08
1 7E-07
NT
NT
1 7E 08
1 7E 08
1 7E 07
NT
33E 07
HT
NT
20E 07
NT
3 7E 09
1 5E-08
NT
flT
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TABLE 2  Average Inhalation Risks and Noncancer HQs in Subarea E2
CHEMICAL
Dichlorodifluoromethane
Dichloroethane. 1.1- (Emylrdene dichlonde)
Dichloroelhane. 1.2-
Dichloroethene. 1,1- (Vmylidine chloride)
Dlchloroethene (bans). 1.2-
Dichlotophanol, 2,4-
Dlchloropropane. 1 ,2- (Propylene dichlorlde)
Dlchloropropene (clj). 1.3-
Dichloroptopene (bans). 1,3-
Drothylphtfialate
Dimethoxybenzidina. 3,3'-
Dimelhylphanol, 2,4-
Dlm«thylphthalat«
Di-n-butytphthalata
Dinrbololuene. 2.6
Dlntoo-2-methytphenol. 4.6-
Dlnrtrophanol. 2.4-
Dlnlbotoluene. 2.4-
Dloxane. 1.4
Di(n)octy1 phthalate
D. 2,4-
Ethyl mathacrylale
Ethyl benzene
Ethytena dibromide
Ethylene oxide
Ethylene Ihlourea
Fluoranthene
Fluoiana
Formaldehyde
Furfural
Heptachlor
Heptachlorobiphenyl
Hexachloroberuene
Hexachloroblphenyt
Hexachlorobutadiana
Haxachlorocyclohaxana, gamma (Lindane)
Hexachlorocyclopentadiene
Hexachloro* thane
Hexachlorophene
Hexanona, 2-
Indenofl ,2.3-cd)pyrene
Isophorone
Malerc hydrazlde
Methoxychlor
Methyl (-butyl ether
Methyl 2 Pentanone. 4 (MIBK)
Methylene chloride
Methylnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nitroanilme 2-
Nttroanilrne 3
Ihhalatton
Slope
Factor
(mg/kg-d)A-1
NA
NA
9 IE 02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
7 8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125 •
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0 000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
OOO005
tlf
Inhalation
RID
(mg/Vg d)
1 4E 02
36E-02
NA
23E 03
50E 03
75E 04
29E 04
1 4E 03
1 4E-03
20E-01
NA
50E-03
NA
25E 02
25E 04
NF
50E 04
50E 04
NA
50E 03
25E 03
2 3E 02
7 1E 02
1 4E-05
NA
20L 05
1 OE 02
1 OE 02
50E 02
3 6E-03
1 3E-04
NA
2 OE-04
NA
5 OE-05
75E 05
50E 06
25E 04
75E05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
tJF
NA
1 OE 02
1 4E 05
I IF
Emission
Rate
(g/sec)
2 5E-04
1 3E 05
1 3E 05
1 3E 05
1 3E-05
55E06
1 3E 05
'1 3E-05
1 3E 05
1 7E 05
1 2E-04
55E08
55E06
1 6E 05
55E 06
55E 06
55E-06
55E 06
49E 04
55E 06
39E 05
25E 04
50E 04
t 2E-04
3 1E-05
1 5E 10
55E 06
6 7E 06
6 1E 04
55E 06
55E 07
1 4E-08
55EX16
1 4E-08
1 OE 04
55E 05
55E 06
55E 06
32E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
E2 avg
E2 avg
E2avg
E2 avg
E2 avg
E2 avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2 avg
E2avg
E2 avg
E2 avg
E2avg
E2avg
E2 avg
EZavg
E2 avg
E2 avg
E2avg
E2 avg
E2 avg
E2 avg
£2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 dvg
Adult
Cancer
Risk
NT
NT
56E 12
74E-11
NT
NT
NT
80E 12
80E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
43E 10
53E-11
NT
NT
NT
1 3E-10
NT
1 2E-11
NT
44E-11
NT
39E-11
NT
NT
38E-I3
NT
NT
NT
NT
NT
NT
NT
NT
3 2E 12
ra
m
NT
NT
NT
Child
Cancer
Risk
NT
NT
1 4E 11
1 8E-10
NT
NT
NT
20E 11
20E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 09
1 3E-10
NT
NT
NT
34E-10
NT
30E-11
NT
1 1E-10
NT
97E-11
NT
NT
95E-13
NT
NT
NT
NT
NT
IIT
ur
MT
8 OF 12
ur
nt
tn
NT
m
School-age
Cancer
Risk
NT
NT
84E 12
1 IE 10
NT
NT
NT
1 2E 11
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
65E-10
79E-11
NT
NT
NT
20E-10
NT
1 8E-11
NT
66E-11
NT
58E-11
NT
NT
5 7E-13
NT
NT
NT
NT
NT
NT
m
NT
4 er 12
NT
(IT
in
NT
UT
Farmer
Cancer
Risk
NT
NT
1 2E 11
1 6E-10
NT
NT
NT
1 8E 11
1 8E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
96E-10
1 2E-10
NT
NT
NT
30E-10
NT
2 7E-11
NT
97E-11
NT
86E-11
NT
NT
84E-13
NT
NT
NT
NT
NT
NT
NT
tJT
7 IE- 12
NT
IIT
III
(IT
m
                                                                                                                                              Adult     Child   School age   Farmer
                                                                                                                                            Noncancer Noncancer Noncancer Noncancer
                                                                                                                                               HQ       HQ       HQ       HQ
66E 07
1 3E 08
NT
2 1E-07
96E 08
28E 07
1 7E4)6
34E4I7
34E4)7
32E^»
NT
4 2E-08
NT
24E^)8
84EXI7
NT
42E-07
42E-07
NT
4 2E 08
60I£4>7
42E07
27E-07
31E-04
NT
28E 10
2 IE 08
2 6E 08
4 7E 07
59E4)B
1 7E-07
NT
1 1E4W
NT
77E4»
2 BE 05
42E^)5
8 4E 07
1 6E 05
NT
NT
5 1E^J9
35E 08
1 7E 08
2 2E 09
8 4E 08
7 1F 08
NT
NT
2 IF 08
1 8F 05
in
25E 06
50E-08
NT
BOE 07
36E 07
1 1E 06
63E06
1 3E 06
1 3E-06
1 2E 08
NT
1 6E-07
NT
9 OE-08
32E-06
NT
16E 06
1 6E-06
NT
1 6E 07
22E06
16E06
10E06
1 2E-03
NT
1 OE 09
79E 08
96E 08
1 7E 06
22E07
63E 07
NT
39E-06
NT
29E 04
10E04
1 6E 04
32E 06
6 IE 05
NT
NT
1 9E 08
1 3E 07
6 IE 08
8 -If 09
3 If 07
2r,r 07
NT
NT
7 9E 08
R 7F (IS
fit
1 5E 06
3 OE 08
NT
4 BE 07
22E 07
63E 07
3 BE 06
76E 07
76E 07
73E-09
NT
95E-OB
NT
54E 08
19E-06
NT
95E 07
95E-07
NT
9 5E 08
1 3E 06
94E 07
60E 07
7 OE-04
NT
6 JE 10
4 BE 08
5 BE 08
1 1E 06
1 3E 07
38E 07
NT
24E 06
NT
1 7E 04
63E 05
95E 05
1 9E 06
3 7E-05
NT
NT
1 2E 08
8 OE 08
3 BE 08
5 If 09
1 9E 07
1 GF 07
NT
NT
4 BE 08
4 IF 05
NT
66E 07
1 3E 08
NT
2 IE 07
96E 08
2 BE 07
1 7E 06
3 4E 07
34E 07
32E-09
NT
4 2E-08
NT
2 4E 08
84E-07
NT
42E 07
4 2E-07
NT
42E 08
60E 07
4 2E 07
27E07
3 1E-04
NT
2 BE 10
2 IE 08
2 6E 08
4 7E 07
59E 08
1 7E 07
NT
1 1E 06
NT
7 7E 05
2 BE 05
42E 05
84E 07
1 BE 05
NT
NT
5 1E 09
35E08
1 7E 08
2 2E 09
8<1E 08
7 IF 08
NT
NT
2 IE 08
1 BF m
tn
Volume V. Appendix V 14
-------
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-------
 TABLE 2  Averagj lnha,..,.on Risks and Noncancei MQs in Subarea E2
CHEMICAL
Nitroaniline. 4-
Nitiobenzeno
Nitrophenot, 2-
Nitrophenol, 4-
N Nrtroso-di-n-butylamlne
N-Ntooso-di-n-propylamina
N-Nitrosodiphenylamine (Diphenylamine)
Nonachforobiphenyl
Octachlofobiphenyl
Pentachlorobenzene
Pantachloroblphanyl
Pentachloronttrobenzane
Pentachlorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl)-1,3 benzodioxole)
Styiene
Tetrachlorobiphenyl
Tetraehloroettiane. 1.1 1.2
Tetrachloroethane. 1,1,2.2-
Tebachloroelhene
Tetrachlorophenol. 2.3.4.6-
Toluene
Trlchloro-1 ,2,2-trifluoroethane. 1 .1 ,2-
Trlchlotobenzene. 1,2.4-
Trichlorobiphenyt
Trichloroelhane. 1,1,1- (Methyl chloroform)
Trlchloroethane. 1,1,2-
Trichloroethene
Trtchlorofluoromethane
Trichlorophenol. 2,4,5-
Trtchlorophenol, 2,4,6-
Vmyl acetate
Vinyl chloride
Xylene. m/p- (m/p Dimethyl benzene)
Kylene, o- (o Dimethyl benzene)
J.3.7.8TCDD
1,2.3. 7.8 PCDD
1.2.34 78-MxCDD
123678 HxCDD
1 .2 3 7 8 9 HxCDD
1.2.3.46 7 8 HpCDD
OCOD
? 3 7 8 TCDF
12378 PCDF
23478 PCDF
123478 HxCDF
123678 HxCDF
? 3 4 6 7 8 H.CDF
Inhalation
Slope
Factor
(mg/kg d)"-1
NF
NA
NF
NF
54E*00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
20E 01
20E 03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E + 05
75E«04
5E»04
5E«04
5E*04
5E»03
5E«02
1 5E«04
75E»03
75E»04
1 5E«04
1 5E»04
1 5E*04
RAC
(mg/m3)
NF
00005
NF '
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02825
NA
0525
002625
NF
025
NA
0 02625
NA
000875
0 02625
0 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
fJA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E-04
7 5E-03
NA
1 5E 01
75E 03
NF
7 1E-02
NA
7 5E-03
NA
2 5E 03
7 5E 03
29E-02
2 1E»00
1 4E-02
NA
7 IE 02
1 OE-03
NA
5 OE-02
25E02
NA
1 4E-02
NA
50E 01
50E-01
NA
NA
NA
NA
NA
rJA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
6 7E 06
55E 06
67E-06
55E 06
1 2E 04
67E 06
67E 06
• 1 4E 08
1 4E-08
48E-05
1 4E 08
34E-05
55E06
67E 06
55E-06
55E 06
1 2E 04
2 3E 05
1 4E 08
55E 06
55E06
5 1E 05
6 BE 06
6 IE 04
33E 04
55E-06
30E 08
t 3E 05
1 3E-05
1 9E 05
2 5E 04
55E-06
55E06
64E 05
2 SE 04
38E 04
55E-06
1 08E 11
678E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 1 5E 09
8 77E It
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2avg
E2avg
E2 avg
E2 avg
E2avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2 avg
E2 avg
E2avg
E2avg
E2avg
E2*vg
E2«vg
E2 avg
E2avg
E2avg
E2avg
E2av0
E2avg
E2avg
E2avg
E2 avg
E2avg
E2avg
E2 avg
E2 avg
E2avg
E2 avg
. E 2 avg
' EZ avg
E2avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2 avg
E2avg
E 2 avg
Adult
Cancer
Risk
NT
NT
NT
NT
32E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E 13
55E 12
5 1E-13
NT
NT
NT
NT
NT
NT
35E-12
55E-13
NT
NT
27E-13
NT
36E-10
NT
NT
80E 12
25E 11
66E 12
1 2E 11
8 IE 12
92E 12
4 5E 12
65E 12
1 3E 11
1 7E 10
1 IE 10
99E 11
1 IE 10
Child
Cancer
Risk
NT
NT
NT
NT
80E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-12
1 4E-11
1 3E 12
NT
NT
NT
NT
NT
NT
B7E 12
1 4E-12
NT
NT
68E-13
NT
90E-10
NT
NT
20E-11
62E-11
1 6E 11
3 IE 11
20E 11
2 3E 11
1 1E-11
1 6E 11
32E I)
4 3E 10
26E 10
25E 10
2 BE 10
School age
Cancct
Risk
NT
NT
NT
NT
4 BE -09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 12
83E 12
7 7E-13
NT
NT
NT
NT
NT
NT
53E-12
82E-13
NT
NT
41E-13
NT
55E-10
NT
NT
1 2E 11
3BE 11
1 OE 11
1 8E 11
1 2E 11
1 IE 11
6 BE 12
98E 12
1 9E 11
26E 10
1 6E 10
1 5E 10
1 7F 10
Farmer
Cancer
Risk
NT
NT
NT
NT
72E-09
NT
NT
NT
NT
NT

NT
NT
NT
NT
NT
NT
NT
NT
16E 12
12E It
1 1E-12
NT
NT
NT
NT
NT
NT
7 BE 12
1 2E-12
NT
NT
60E-13
NT
81E-10
NT
NT
1 BE- 11
56E 11
1 5E-11
2 7E 11
1 8E 11
20E 11
1 OE 11
1 4E 11
2 81 1 1
38L 10
2 3E 10
2 2E 10
? *>( 10
                                                                                                                                                Adult      Child    School-age   Farmer
                                                                                                                                              Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                 HO        HQ       HQ       HQ
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-06
2 8E-06
NT
1 4E 09
2 BE -08
NT
1 2E-08
NT
28E-08
NT
79E-07
3 5E 08
8 2E 07
59E-09
1 5E4)8
NT
67E-09
48E-07
NT
1 9E-07
84E-09
NT
1 7E-OT
NT
2 9E-08
42E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
HI
NT
III
111
NT
SSE 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E 06
1 1E-07
NT
53E 09
1 IE 07
NT
4 5E-08
NT
1 1E-07
NT
29E 06
1 3E 07
3 IE 06
2 2E 08
5 5E-08
NT
25E 08
1 8E 06
NT
TOE 07
32E08
NT
64E 07
NT
1 IE 07
1 6E 09
NT
NT
NT
NT
m
til
III
til
Ml
III
III
III
111
NT
33E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E 06
6 3E-08
NT
32E 09
6 3E-08
NT
2 7E-08
NT
6 3E-08
NT
1 BE 06
7 BE 4)8
1 9E06
1 3E 08
3 3E-08
NT
1 5E 08
1 1E-06
NT
4 2E 07
1 9E 08
NT
3 9E-07
NT
66E 08
95E 10
NT
NT
NT
NT
NT
NT
NT.
NT
NT
NT
NT
III
NT
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-06
2 BE -08
NT
1 4E09
2 BE 4)8
NT
1 2E-08
NT
2 BE 4)8
NT
79E4>7
3 5E 08
82E4J7
59E4J9
1 5E-08
NT
67EO9
48E4J7
NT
1 9E4J7
84E-09
NT
1 7E-07
NT
2 9E 08
42E 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
/olume V  Appendix V-14
-------
TABLE 1  Average Inhalation Risks and Noncancec HQs in Subaiea E2
CHEMICAL
1 2.3 7,8.9 HxCDF
1 2.3,4.6.7,8 HpCDF
1.2.3.4. 7.8.9 HpCDF
OCDF
Dloxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
•ad
Mercury (and MeHg)
Jickel
ielenium
Silver
hallium
inc
lydrogan chloride
otal nitrogen oxides (NO*)
otal sulfur oxides (SOx)
'articulate matter
:espirable particulates
Inhalation
Slope
Factor
(mg/kg d)«-1
1 5E+04
1 5E+03
1 5E»03
1 5E»02

NA
MA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA .
NA

NA
000035
0000263
0000125
0 004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E05
36E 05
1 3E 03
1 3E-04
1 3E-03
25E01
NA
NA
2 IE 05
5 OE-03
1 3E 03
1 3E-03
1 BE 05
7 5E 02
50E04
NA
NA
NA
NF
Emission
Rale
(g/sec)
293E-10
9 30E-09
1 22E 09
1 89E-06
4 28E-08
24E-04
42E-06
37E4J5
1 5E-04
33E^>8
16E-OS
7 1E-07
71E-07
94E-05
43E-05
1 4E 03
50E-06
47E-04
1 5E-05
34E^)5
1 2E 04
32E 02
24E«00
9 IE 02
7 2E 02
7 2E 02
Subarea
E2 avg
E2 avg
E2avg
E2 avg

E2avg
E2avg
E2avg
E2 avg
E2 avg
E2avg
E2avg
E2avg
E2 avg
E2 avg
E2avg
E2avg
E2avg
E2 avg
E2avg
E2 avg
E2avg
E2 avg
E2avg
E2avg
E2avg
Off site
Vapor
Cone
(ug/m3)
4 IE-11
1 3E 09
1 7E-10
2 7E-09
60E-09
34E05
59E^)7
52E06
2 IE 05
46E-09
22E-06
99E-08
99E08
1 3E-05
60E06
2 OE-04
70E07
66E 05
2 1E4»
48E-06
1 7E-05
45E^)3
34E 01
1 3E-02
1 OE 02
1 OE-02
Cancer
Adult
Dose
(mg/kg d)
1 4E-15
46E 14
60E 15
93E 14
2 1E-13
1 2E-09
2 IE-11
1 8E-10
74E-10
16E-13
79E-11
35E-12
35E-12
46E-10
2 1E-10
69E-09
25E-11
23E09
74E 11
1 7E 10
59E-10
1 6E-07
1 2E-05
4 5E-07
3 5E 07
3 5E-07
Cancer
Child
Dose
(mg/kg-d)
36E 15
1 IE 13
1 5E 14
23E 13
53E-13
29E 09
52E-H
45E-10
1 8E 09
4 1E-13
20E-10
87E-12
87E 12
1 2E-09
53E-10
1 7E-08
6 IE-11
58E-09
1 8E-10
42E-10
1 5E4»
39E-07
30E-05
1 1E-06
8 BE -07
8 8E-07
Cancer
School-age
Dose
(mg/kg-d)
22E 15
69E 14
9 IE-IS
1 4E 13
32E-13
1 8E-09
3 IE-11
27E-10
1 1E-09
24E-13
1 2E-10
53E-12
53E-12
70E-10
32E-10
1 OE 08
37E-11
35E-09
1 IE 10
25E 10
89E-10
2 4E 07
18E-05
6 8E 07
5 3E 07
5 3E-07
Cancer
Farmer
Dose
(mg/kg-d)
32E 15
1 OE 13
1 3E 14
2 IE 13
4 7E 13
26E-09
46E-11
4 1E-10
1 6E-09
36E-13
18E-10
78E-12
78E-12
1 OE 09
47E-10
1 5E-08
55E-11
51E-09
1 6E 10
37E-10
1 3E-09
35E-07
27E-05
10E-06
79E-07
7 9E-07
Noncancer
Adult
Dose
(mg/kg d)
1 IE 14
36E 13
47E 14
73E-13
16E 12
92E09
16E 10
14E09
58E09
1 3E-12
6 IE 10
27E 11
27E-11
36E09
16E-09
54E-08
1 9E-10
18E-06
5 BE 10
1 3E-09
46E 09
12E-06
93E05
35E-06
28E06
2 BE -06
Noncancer
Child
Dose
(mg/kg-d)
42E 14
1 3E 12
1 7E-13
2 7E 12
6 IE-12
34E 08
60E 10
53E 09
2 IE 08
47E-12
23E-09
10E-10
10E 10
1 3E 08
62E-09
2 OE 07
72E 10
6 7E 08
2 IE 09
49E09
1 7E 08
46E 06
35E04
13E 05
1 OE 05
1 OE 05
Noncancer
School-age
Dose
(mg/kg-d)
25E-14
8 IE 13
1 IE 13
16E 12
37E 12
2 1E-08
36E-10
32E09
1 3E-08
29E-12
1 4E 09
6 IE 11
6 IE 11
81E-09
37E09
1 2E-07
43E-10
4 1E 08
1 3E-09
29E 09
10E-OB
2 BE 06
2 IE 04
79E^»
62E 06
6 2E 06
Noncancer
Farmer
Dose
(mg/kg d)
1 IE 14
36E 13
47E-14
73E-13
16E-12
92E-09
1 6E-10
ME 09
5 BE 09
1 3E-12
6 IE 10
27E 11
27E 11
36E09
16E 09
5 4E 08
19E 10
1 8E^)B
5 BE 10
1 3E-09
46E 09
1 2E4W
93E4M
35E06
2 BE 06
28E^»
  OTES
  NA > Not applicable
  NF * Not found
  NT - No toxlcrry information
  HQ c Hazard quotient
  HI - Hazard Index
  lume V. Appendix V '
-------
TABt E 2  Average Inhalauon Risks and Noncancei HQs in Subaiea E 2
CHEMICAL
1.2,3. 7,8.9 HxCDF
1.2 3.4 6,7.8 HpCDF
1. 2.3.4. 7.8,9-HpCDF
CCDF
Dloxin TEO
Aluminum
Antimony
A/sente
Barium
Beryllium
Cadmium
C.iromium (hexavalent)
Chromium (trivalent)
Copper
_ead
Mercury (and MeHg)
Mlcket
Selenium
Silver
Thallium
line
-tydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SO*)
'articulate matter
^espirable participates
Inhalation
Slope
Factor
(mg/kg-d)"-1
1 5E+04
1 5E»03
1 5E»03
1 5E+02

MA
MA
SO
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE4M
75E-05
36E-05
1 3E-03
1 3E-04
1 3E-03
2 5E-01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E-03
1 BE 05
75E-02
5 Of -04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E 10
930E 09
1 22E-09
1 89E 08
4 28E-08
2 4E-04
42E06
37E-05
1 5E 04
33E-08
16E-05
71E07
7 1E-07
94E-05
43E05
1 4E-03
50E 06
47EXM
1 5E 05
34E 05
12E^4
3 2E 02
24E+00
91E-02
7 2E 02
72E4)2
Subarea
E2avg
E2 avg
E2 avg
E2avg

E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
E2avg
Adult
Cancer
Risk
22E-11
69E 11
90E 12
1 4E 11
69E 10
NT
NT
9 1E-09
NT
1 4E-12
48E 10
1 4E-10
NT
NT
NT
NT
2 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
54E 11
1 7E 10
22E 11
35E 11
1 7E 09
NT
NT
23E-08
NT
34E-12
1 2E 09
36E-10
NT
NT
NT
NT
52E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
33E 11
1 OE 10
1 4E 11
2 IE 11
1 OE 09
NT
NT
14E-08
NT
21E-12
72E-10
22E-10
NT
NT
NT
NT
31E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
48E-11
1 5E-10
20E 11
3 IE 11
1 5E-09
NT
NT
20E-O8
NT
30E-12
1 1E-09
32E-10
NT
NT
NT
NT
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
 «/OTES
  NA - Not applicable
  NF « Not found       ";
  NT * No toxkity Information
  HO <* Hazard quotient
  HI •= Hazard index
                                                                                Total Risk   1 5E-08    38E08    2 3E-08    3 4E-08
                                                                                                                                               Adult      Child    School age   Farmer
                                                                                                                                             Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                HQ       HQ       HQ       HQ
NT
NT
NT
NT
NT
NT
1 BE 06
1 9E 05
1 6E-04
1 OE 09
49E06
2 2E 08
1 1E-10
NT
NT
25E-03
3 BE 4)8
1 4E-05
46C-07
74E4K
6 1E-08
25E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E 06
7 IE 05
60E-04
38E09
18E-05
8 IE 08
41E-10
NT
NT
9 4E 03
1 4E 07
54E05
1 7E 06
2 BE 04
2 3E-07
9 2E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E06
43E 05
36E04
23E09
1. IE-OS
49E08
25E-10
NT
NT
5 7E 03
B 7E 08
33E05
10E4»
1 7E 04
1 4E 07
55E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E 06
1 9E 05
1 6E 04
1 OE 09
49E^)6
22E08
1 1E-10
NT
NT
25E4I3
38E08
1 4E-05
46E 07
74E05
6 1E 08
25E03
NT
NT
NT
NT
                                                                                                                                     Total HI    59E4W    22E02    1 3E 02    5 9E 03
 olume V. Appendix V-14
-------
Noncancer Noncancer
School age Faimet
Dose Dose
(mg/kg d) (mg/kg d)
oncanc
Child
Dose
mg/kg-d
ncance
Adult
Dose
g/kg-d
Cancer Cancer
School age Faimet
Dose Dose
(mg/kg d) (mg/kg-d)
 C S.
 u °
RAC
mg/m3)
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-------
TABLE 3  Aveiago InhV    ,.i'Risks and Noncancer HQs m Subaiea E3
CHEMICAL
Acenaphthene
Acenaphthylene
^cetaldehyde
Acetone
^cetophenone
Acrylonrtrile
tathracene
Benzene
Benzole acid
Benzotrlchlotide
3enzo(a)anthracene
3enzoja)pyr«ne
3enzo(b)fluoranthene
3enzo(g ,h ,l)perylene
3enzo(k)fluoranmene
3ls(2-chloroethoxY) methane
3is(2-chloroethyl)ether
3ls(2-chloroisopropy1)ether
3ls(2-ethylhexyl)phthalale
3romodlchloromethane
3romoform
Sromomethane
3romodipheny1 ether, p-
autnnone. 2- (Methyl ethyl ketone)
Jutylbenzylphthalale
Carbon disulfide
Carbon tebichlorlde
3hlordane
^hloro-3-methylphenol, 4-
;htoroaniline. p- (4-Chloroaniline)
~hlorobenzene
"hlorobenzilate
;hloroethane (Ethyl chloride)
Chloroform
;hloromethane
;hloronaphthalene, beta
;hlorophenol. 2-
^hlorodiphenyl ether. 4- *:
"hrysene
'resol. m-
;resol. o- (2-Methylphenol)
:resol. p-
;iotonaldehyde
lumene
3DE.4.4'-
3iberu(a,h)anthracene
}ibromochloromethane
Dichlorobenzene. 1.3-
}ichloiobenzene. 1.4-
Jichlorobenzene. 1.2-
3tchloiobenzidme 3,3'-
Oichloiobiphenyl
Inhalation
Slope
Factor
NA
NF
7 7E 03
NA
NA
2 4E-01
NA
2 9E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E*00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
5 3E 02
1 3E»00
NF
NA
NA
2 7E-01
NA
81E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
C0025
00005
0000053
NF
00035
OOO5
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
?0 00275
NA
NA
00175
MA
02
005
MA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
2 5E 02
1 4E 04
75E02
43E-04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE-02
50E 03
50E 03
50E 03
3 BE 04
NA
7 1E 02
50E 02
7 IE 04
1 4E^)4
1 5E-05
NF
1 OE 03
1 4E 03
5 OE-03
71E-01
2 5E-03
NA
2 OE 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
64E 04
MA
MA
50E 03
NA
5 7E 02
1 4E 02
NA
MA
Emission
Rate
(g/sec)
67E-06
6 7E-06
30E 04
2 9E 03
2 9E 04
2 OE 04
55E-06
,1 5E 05
1 1E-05
32E05
55E-06
55E-06
55E-06
55E-08
55E 06
6 7E 06
1 3E-05
87E-06
37E-05
1 OE 04
55E-06
49E04
67E 06
5 1E-05
55E-06
89E 05
1 6E-04
55E 07
67E 06
6 7E-06
55E-06
37E 05
49E 04
2 7E 04
2 5E 04
67E 06
55E 06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
E3avg
E3 avg
E3 avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3 avg
E3avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3 avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E3 avg
E 3 avg
Adult
Cancer
Risk
NT
NT
49E-12
NT
NT
1 OE-10
NT
90E-13
NT
NT
NT
NT
NT
NT
NT
NT
3 1E 11
NT
NT
NT
45E-14
NT
NT
NT
NT
NT
1 8E 11
1 5E-12
NT
NT
NT
2 1E-11
NT
45E-11
33E 12
NT
NT
NT
NT
NT
NT
NT
MT
NT
MT
MT
MT
MT
tlT
MT
MT
MT
Child
Cancer
Risk
NT
NT
1 2E-11
NT
NT
25E-10
NT
22E-12
NT
NT
NT
NT
NT
NT
NT
NT
7 7E-11
NT
NT
NT
1 1E 13
NT
NT
NT
NT
NT
44E 11
37E-12
NT
NT
NT
53E-11
NT
1 IE 10
8 1E-12
NT
NT
NT
NT
NT
NT
NT
MT
MT
MT
MT
MT
MT
MT
MT
MT
Ml
School age
Cancer
Risk
NT
NT
74E-12
NT
NT
1 5E-10
NT
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
4 7E-11
NT
NT
NT
67E-14
NT
NT
NT
NT
NT
26E 11
23E-12
NT
NT
NT
32E-11
NT
6 BE 11
49E-12
NT
NT
NT
NT
NT
NT
NT
I4T
MT
NT
MT
MT
MT
Ml
IIT
MT
MT
Farmer
Cancer
Risk
NT
NT
1 1E-11
NT
NT
23E-10
NT
20E-12
NT
NT
NT
NT
NT
NT
NT
NT
69E-11
NT
NT
NT
99E-14
NT
NT
NT
NT
NT
39E-11
33E-12
NT
NT
NT
47E-11
NT
1 OE-10
72E-12
NT
NT
NT
NT
NT
NT
NT
NT
Ml
MT
MT
MT
MT
MT
MT
MI
MT
                                                                                                                                             Adult      Child    School age   Faimer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ       HQ       HQ       HO
7 3E-09
NT
77E 06
1 9E-06
1 9E-07
2 3E-05
1 2E-09
5 6E 07
1 9E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-08
1 2E-07
34E^)7
1 BE 08
23E-05
NT
t 2E-08
1 BE -09
2 1E-06
1 BE 05
60E-07
NT
1 1E-07
6 3E-08
1 2E-07
1 1E-08
1 7E-06
NT
55E09
72E-08
NT
NT
7 2E 09
7 2E 09
72E-08
NT
1 4E 07
MT
MT
8 6F 08
MT
1 6f 09
6 IF 09
MT
MT
2 7E 08
NT
29E 05
7 IE 06
7 2E 07
8 7E 05
4 5E 09
2 1E-06
69E 10
NT
NT
NT
NT
NT
NT
NT
NT
4 IE 08
46E 07
1 3E 06
6 BE 08
84E-05
NT
4 4E 08
68E09
77E 06
6 BE 05
23E-06
NT
4 1E 07
24E 07
45E07
42E 08
65E 06
NT
2 IE 08
2 7E 07
NT
NT
27E 08
2 7E 08
2 7F. 07
NT
5ir 07
MT
Ml
3?l 07
Ml
5 91 09
7 V 01
MT
Ml
1 7E 08
NT
1 7E 05
43E06
4 3E 07
52E 05
2 7E 09
1 3E 06
42E 10
NT
NT
NT
NT
NT
NT
NT
NT
25E-08
2 BE 07
7 7E 07
4 IE 08
5 IE-OS
NT
27808
4 IE 09
4 BE 06
41E05
1 4E-O6
NT
2 5E 07
1 4E 07
27E 07
25E 08
39E 06
NT
1 2E 08
1 6E 07
NT
NT
1 6E 08
1 6E 08
1 BF 07
NT
3 ?F 07
MT
MT,
2 OF 07
MT
3 6E 09
1 4F 08
MT
MT
7 3E-09
NT
7 7E 06
1 9E 06
1 9E 07
2 3E 05
1 2E 09
56E07
1 9E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 08
1 2E 07
34E07
1 8E48
23E-05
NT
1 2E 08
1 BE 09
2 IE 06
1 BE 05
80E 07
NT
1 IE 07
63E 08
1 2E 07
1 IE OB
1 7E 06
NT
55E 09
7 2E 08
NT
NT
72E 09
72E 09
72E 08
NT
1 4E-07
NT
m
8 fiF Ofl
NT
1 6E 09
B IF. 09
MT
fIT
 'olum« V. Appendix V 14
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-------
TABLE 4  Average Inhalation Risks and Noncaneei HQs in Subarea Nl
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acelophenona
Acrylonitrile
Anthracene
Benzene
Benzole acid
Benzotoichtoride
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluofanthene
9enzo(g ,h ,l)peryl«n«
Benzo(k)fluoranlh«ne
Bis(2-chloroethoxy) methane
Bis(2-chloroethyt)ether
Bis(2 -chlorolsopropyl)ether
3is(2-ethylhexyt)phthalate
3romodichloromethane
Bromolorm
3romomethana
Jromodiphenyt ether . p
Jutanone. 2- (Methyl ethyl kelone)
Jutylbenzylphttialate
Carbon disurfide
Carbon tetrachloride
;hlordane
;hloro-3-m«thy1pr,enol, 4-
:hloroanillne, p- (4-Chloroaniline)
rhlorobenzon*
:hlorobenzilat«
;hloioethane (Ethyl chloride)
Chloroform
:hlorometh»ne
;hloronaphttialene. beta
'.hlorophenol, 2-
:hlorodiphenyf ether. 4- ..
;hrysene
;resol, m-
:iesol. o- (2-Methylphenol)
;resol. p-
:rotonaldehyde
lumene
IDE, 4.4'-
>ibenz(a.h)anthrac»ne
nbromochloromelhane
iichlorobenzene 13
nchloiobenzene. 1.4-
hchlorobenzene. 1 .2-
uchlorobenzidme 3 3'-
nchloiobiphenyl
Inhalation
Slope
Factor
(mg/kg d)"-1
NA
NF
7 7E-03
NA
NA
2 4E-Ot
NA
2 9E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
3 9E 03
NA
NA
NA
NA
NA
53E-02
1 3E»00
NF
NA
NA
2 7E-01
NA
6 IE 02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA -
NA
NA
NA
RAG
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RfD
(mg/kg d)
1 5E-02
NF
64E 04
2 5E 02
25E02
1 4E 04
7 5E-02
43E 04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E 03
50E 03
36E 04
NA
7 IE 02
50E 02
7 IE 04
1 4E 04
1 5E 05
NF
1 OE 03
1 4E 03
5 OE-03
7 16-01
2 5E-03
NA
20E 02
1 3E-03
NF
NA
1 3E-02
1 3E 02
1 3E-03
NA
64E 04
NA
NA
50E 03
NA
5 7E 02
1 4E 02
NA
NA
Emission
Rale
(g/sec)
67E06
67E06
30E 04
2 9E 03
2 9E 04
2 OE-04
55E06
1 5E 05
1 IE 05
3 2E 05
55E06
55E-06
55E06
55E06
55E-06
67E-06
1 3E 05
6 7E-06
3 7E 05
1 OE-04
55E 06
49E 04
6 7E 06
5 IE 05
55E 06
89E-05
1 6E-04
55E 07
67E 06
6 7E 08
55E-06
37E-05
4 9E-04
2 7E-04
25E 04
67E 06
55E06
67E06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E-08
Subarea
N1 avg
Nt avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Nt avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Nt avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
;NI avg
N1 avg
N1 avg
N1 avg
N1 avg
Nt avg
Ml avg
Nl avg
Ml avg
HI avg
m avg
Adull
Cancel
Risk
NT
NT
1 1E-11
NT
NT
24E-10
NT
2 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
72E-11
NT
NT
NT
10E 13
NT
NT
NT
NT
NT
4 IE 11
35E 12
NT
NT
NT
50E-11
NT
1 1E-10
76E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
28E-11
NT
NT
59E-10
NT
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 BE 10
NT
NT
NT
26E 13
NT
NT
NT
NT
NT
1 OE 10
87E-12
NT
NT
NT
1 2E-10
NT
26E 10
1 9E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Nl
NT
NT
Nl
School age
Cancel
Risk
NT
NT
1 7E-11
NT
NT
36E-10
NT
32E 12
N',
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
16E-13
NT
NT
NT
NT
NT
62E 11
53E-12
NT
NT
NT
75E-11
NT
1 6E-10
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
in
tlf
Nl
NT
NT
tit
Farmer
Cancer
Risk
NT
NT
25E-11
NT
NT
53E-10
NT
4 7E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
2 3E-13
NT
NT
NT
NT
NT
9 IE 11
78E-12
NT
NT
NT
1 1E-10
NT
23E-10
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
in
NT
NT
NT
III
NT
                                                                                                                                              Adull      Child    School-age   Farmer
                                                                                                                                            Noncancer Noncancer Noncancer Noncancer
                                                                                                                                               HO        HQ        HQ       HQ
1 7E-08
NT
1 BE 05
44E 06
4 5E-07
5 4E 05
2 BE 09
1 3E-06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 6E-08
2 9E-07
7 9E-07
42E08
5 3E-05
NT
2 BE 08
42E09
4 BE 06
42E05
1 4E 06
NT
2 6E-07
1 5E-07
2 BE 07
2 6E 08
41E-06
NT
1 3E 08
1 7E-07
NT
NT
1 7E 08
1 7E-Q8
1 7E-07
NT
33E 07
NT
NT
20E-07
NT
3 7E 09
1 5F 08
NT
Nl
6 4E-08
NT
67E-05
1 7E-05
1 7E-06
2 OE 04
1 IE 08
49E06
1 6E-09
NT
NT
NT
NT
NT
NT
NT
NT
96E08
1 1E-06
30E06
1 6E 07
2 OEM
NT
1 OE 07
16E08
1 BE -05
1 6E 04
53E-06
NT
96E07
55E-07
1 1E 06
98E08
1 5E-05
NT
4 BE 08
6 3E-07
NT
NT
63E 08
63E 08
63E-07
NT
1 ?F 06
NT
NT
7 M" 07
NT
1 4f 08
5 r>f. 08
fit
HI
39E 08
NT
4 IE 05
1 OE 05
1 OE 06
1 2E 04
63E-09
30E-06
98E-10
NT
NT
NT
NT
NT
NT
NT
NT
5 BE 08
64E-07
1 BE 06
95E-08
12E^)4
NT
62E08
9 5E-09
1 1E 05
96E 05
32E-06
NT
58E 07
33E 07
64E07
59E 08
92E06
NT
2 9E 08
3 8E-07
NT
NT
3 BE 08
38E 08
3 BE 07
Nf
74E 07
NT
NT
4RF 07
NT
8 3E 09
3 IF. 08
NT
in
1 7E-08
NT
1 BE 05
44E06
4 5E-07
5 4E 05
2 BE 09
1 3E 06
4 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 6E 08
29E 07
79E 07
4 2E 08
53E-05
NT
2 BE 08
42E09
48E06
4 2E 05
1 4E-06
NT
26E 07
1 5E 07
2 BE 07
2 6E 08
4 1E-06
NT
1 3E 08
1 7E 07
NT
NT
1 7E 08
1 7E 08
1 7E 07
NT
33F 07
NT
NT
20E 07
NT
37E 09
1 5F 08
NT
NT
 jlurne V Appendi« V
-------
TABLE 4  Average lnr>_ _,i6n Risks and Noncancer HQs in Subaiea N1
CHEMICAL (
Dichlorodifluoromethane
Dichloroethan*. 1.1- (Ethylidene dichloride)
Dichloroethan*. 1,2-
Dlchloroetnene. 1,1- (Vlnylidine chloride)
Dlchloroethene (bans), 1 .2-
Dichlorophenol. 2,4-
Dichloropropane. 1,2- (Propylene dichloride)
Dlchloropropen* (els), 1.3
Dichloropropen* (trans), 1 .3-
DUthylphthalat*
Dtmethoxybenzldlne. 3.3'-
Dlmethylphenol. 2.4-
Dfmethylphthalat*
CM-n-butytphthatate
Dinrtrololuene. 2,6-
Dlnrtto-2-methytphenol. 4.6
Dinttrophenol. 2.4-
Dinrtjotoluene. 2.4-
Dioxane. 1.4-
Dl(n)octy) phthalate
D, 2,4-
Ettiyl methacrylata
E Ihylbenzefia
Ethylene dibromlde
Ethylena oxide
Ethylehe thlourea
Fluoranthene
Fluor ene
Formaldehyde
Furfural
Heptachlor
Heptachloroblphenyl
Hexachloroberuene
Hexachloroblphanyl
Hexachlorobutadiena
Hexachlorocyclohexane. gamma (Llndane)
Hexachlorocyclopentadiene
Hexachloroethana *•
Haxachlorophene
Hexanone, 2-
lndeno(1 ,2,3-cd)pyr*ne
Isophorone
Malalc hydrazide
Methoxychlor
Methyl t butyl ether
Methyt-2-Pentanone. 4- (MIBK)
Methylene chloride
Methylnaphthalene, 2-
Monochlorobiphenyt
Naphthalene
Nitroaniline. 2-
Nitroamline, 3-
Inhalation
Slope
Factor
mg/kg-d)A-1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
35E-01
NA
NA
NA
4 5E-02
NA
45E+00
NA
16E+00
NA
7 8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E 03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA ••
0007875
00175
0 002625
0001
0005
0005
0.7
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
OOOO05
NA
000007
0035
0035
0.175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
0 75
NF
NA
0035
000005
NF
Inhalation
RtD
(mg/kg-d)
1 4E-02
3 6E-02
NA
2 3E-03
50E 03
75E 04
2 9E 04
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
2 5E-02
2 5E-04
NF
5 OE-04
5 OE-04
NA
2 5E 03
2 3E 02
7 IE 02
1 4E-05
NA
20E 05
1 OE 02
1 OE 02
5 OE-02
36E 03
1 3E-04
NA
2 OE-04
NA
50E 05
7 5E-05
50E 06
2 5E 04
7 5E-05
NF
NA
5 OE 02
1 3E-01
1 3E 03
2 IE 01
5 7E 03
2 1E-01
NF
NA
10E 02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E 04
1 3E-05
1 3E-05
1 3E-05
1 3E-05
55E-06
3E-05
3E05
7E-05
2E-04
55E-06
S5E-06
16E-05
55E-06
55E-06
55E-06
55E-06
4 9E-04
55E06
2 5E-04
5 OE-04
1 2E4)4
3 IE-OS
1 5E-10
55E-06
67E-06
61E-04
55E-06
5 5E-07
1 4E-08
55E 06
1 4E-08
1 OE-04
55E-05
55E-06
55E06
32E-05
64E 05
55E-06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
Nl avg
N1 avg
Nl avg
Nl avg
Nl avg
Nl avg
N1 avg
Nl avg
Nl avg
Nlavg
Nl avg
Nl avg
Nlavg
Nl avg
Nlavg
N1 avg
Nl avg
Nl avg
N1 avg
Nl avg
Nl avg
N1 avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
N1 avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
N1 avg
Nl avg
Nl avg
Nl avg
Nl avg
N1 avg
Nl avg
N1 avg
Nl avg
N1 avg
Nl avg
Nl avg
Nt avg
HI avg
Nt avg
Nt avg
HI avg
Nl avg
Ofl-site
Vapor
Cone
(ug/m3)
34E 05
1 BE 06
1 8E-06
1 BE 06
1 BE 06
7 7E-07
1 BE 06
1 BE -06
1 8E-06
24E-06
1 6E-05
7 7E-07
7 7E-07
22E-06
7 7E-07
77E-07
7 7E-07
7 7E-07
69E45
7 7E-07
54E 06
34E4I5
70E-05
1 6E-05
43E-06
2 OE-11
7 7E-07
9 4E-07
85E-05
7 7E-07
7 7E-08
2 OE-09
7 7E-07
2 OE-09
1 4E-05
77E06
7 7E-07
7 7E 07
45E 06
90E 06
77E 07
94E 07
1 6E 05
7 7E 08
1 BE 06
1 BE 06
55E 05
59E 06
2 3E 09
7 7E 07
94E 07
94E 07
Cancer
Adult
Dose
(mg/kg-d)
1 2E 09
62E-11
62E-11
62E-11
62E-11
27E-11
62E-11
62E-11
62E-11
83E-11
57E-10
27E-11
27E-11
77E-11
27E-11
27E-11
27E-11
27E-11
24E-09
27E-11
19E-10
1 2E-09
25E-09
57E-10
1 5E-10
72E-16
27E-11
33E 11
3 OE-09
27E-11
27E-12
69E-14
27E-11
69E 14
50E-10
27E-10
27E-11
27E-11
1 6E-10
32E-10
27E 11
33E 11
57E 10
2 7E 12
62E 11
62E 11
20E 09
2 IE 10
82E 14
2 7E 11
33E 11
33E It
Cancer
Child
Dose
(mg/kg-d)
3 OE-09
15E-10
1 5E-10
1 5E-10
1 5E-10
68E-11
1 5E-10
1 5E-10
1 5E-10
2 1E-10
1 4E-09
68E-11
68E-11
1 9E-10
68E-11
68E-11
66E-11
68E-11
61E-09
68E-11
48E-10
3 OE-09
61E-09
1 4E-09
37E-10
1 BE 15
68E-11
82E-11
75E-09
68E-11
68E-12
1 7E-13
68E-11
1 7E-13
1 2E-09
67E-10
68E-11
6 BE 11
39E-10
79E 10
6 BE 11
82E-11
1 4E 09
68E 12
1 5E 10
1 5E 10
49E 09
5 IE 10
20E 13
6 BE 11
82E 11
82E 11
Cancer
School-age
Dose
(mg/kg d)
1 8E-09
93E-11
93E-11
93E-11
93E-11
41E-11
93E-11
93E 11
93E-11
1 3E-10
85E-10
1E-11
1E-11
2E-10
1E-11
1E-11
1E-11
1E-11
37E-09
4 1E-11
29E-10
1 BE 09
37E-09
85E-10
23E-10
1 1E-15
4 1E-11
5 OE-11
45E-09
41E-11
4 1E-12
1 OE-13
41E-11
1 OE-13
75E-10
41E-10
41E-11
4 1E-11
24E-10
48E-10
4 1E-11
50E 11
BSE 10
4 IE 12
93E 11
93E 11
29E 09
3 1E 10
1 2E 13
4 IE 11
50E 11
50E 11
Cancer
Farmer
Dose
(mg/kg-d)
2 7E-09
1 4E-10
4E-10
4E-10
4E-10
OE-11
4E-10
4E-10
4E-10
BE 10
3E-09
60E-11
6 OE-11
1 7E-10
6 OE-11
6 OE-1 1
6 OE-11
6 OE-11
54E-09
6 OE-11
43E-10
27E-09
5 5E-09
1 3E 09
33E-10
1 6E-15
6 OE-11
73E-11
66E-09
6 OE-11
60E-12
15E-13
6 OE-11
1 5E 13
1 1E-09
60E-10
6 OE-11
6 OE-11
35E-10
70E-10
6 OE-11
73E 11
1 3E 09
60E 12
1 4E 10
1 4E 10
4 3E 09
46E 10
1 BE 13
60E 11
7 3E 11
7 3F 11
Noncancer 1
Adult
Dose
(mg/kg-d)
9 4E-09
4 BE 10
48E-10
4 BE 10
48E-10
21E-10
4BE-10
4BE-10
4 BE 10
65E-10
4 T-09
2 IE 10
21E-10
60E-10
21E-10
21E-10
2 IE-ID
21E-10
19E-08
21E-10
15E-09
04E4)9
1 9E-08
44E 09
12E-09
56E 15
2 1E-10
26E-10
23E48
21E-10
2 1E-11
54E-13
21E-10
54E 13
39E-09
2 1E-09
2 IE 10
2 IE 10
1 2E-09
2 5E-09
2 IE 10
26E-10
44E 09
2 1E-11
4 BE 10
4 BE 10
1 5E 08
1 6E 09
64E 13
2 IE 10
26E 10
26F 10
Noncancer 1
Child !
Dose
(mg/kg-d)
3 5E 08
1 BE 09
1 BE 09
1 8E 09
1 BE 09
79E-10
1 8E-09
18E09
1 BE -09
24E-09
16E-08
79E-10
79E-10
2 2E-09
79E-10
79E-10
79E-10
79E 10
7 IE-OS
79E-10
56E-09
35E-08
71E-08
16E48
2 IE 14
79E-10
96E-10
8 7E-08
79E-10
79E-11
20E-12
79E 10
20E-12
1 4E 08
79E09
79E 10
79E-10
46E 09
92E09
79E 10
96E 10
1 6E 08
79E 11
1 BE 09
1 BE 09
5 7E 08
6 OE 09
2 4E 12
79E 10
96E 10
96F 10
-loncancei Noncancer
>chool-age Farmer
Dose Dose
(mg/kg d) (mg/kg d)
2 IE 08 94E09
1 1E 09 48E-10
1 IE 09 48E-10
1 1E-09 48E-10
1 IE 09 48E-10
48E-10 2 IE 10
11E09 4 BE 10
11E09 48E-10
1 1E-09 4 BE 10
15E09 85E-10
1 OE 08 4 4E 09
48E-10 2 IE 10
48E-10 2 IE 10
1 4E-09 60E-10
48E-10 2 IE 10
4 BE 10 2 IE 10
4 BE 10 2 1E-10
48E-10 21E-10
4 3E-08 1 9E-08
48E-10 2 1E-10
34EO9 1SE-09
2 1E-08 94E49
4 3E-08 1 9E-08
1 OE 08 4 4E 09
2 6E-09 1 2E 09
1 3E 14 56E-15
48E10 2 IE 10
5BE-10 26E-10
5 3E-08 2 3E-08
4 BE 10 2 IE 10
4 BE 11 2 IE-It
1 2E-12 54E-13
48E10 21E-10
1 2E-12 54E-13
87E09 39E-09
4 7E-09 2 1E-09
4 BE 10 2 IE 10
4 BE 10 2 IE 10
2 BE 09 1 2E-09
56E09 25E-09
4 BE 10 2 IE 10
5 BE 10 26E10
1 OE 08 44E09
48E11 2 IE 11
1 1E 09 4 BE 10
" 1 1E 09 4 BE 10
3 4E 08 1 5E 08
3 BE 09 1 6E 09
1 4E 12 64E 13
4 BE 10 2 1E 10
5 BE 10 26E 10
5 BE 10 26F 10
Volume V. Appendix V-14
-------
  TABLE 4  Average Inhalation Risks and fJoncancer HQs in Sub.nea Nl
CHEMICAL
Dichlorodifluoromethane
Dichloroethane. 1.1- (Ethylidene dichlonde)
Oichloroethane. 1 .2-
Dichloroethene, 1.1- (Vinylidme chloride)
Dichloroethene (trans). 1.2-
Oichlorophenol. 2.4-
Dichlofopropane 1,2- (Prop/tone dichlonde)
Dichloropropen* (cis). 1.3-
Dichloropropene (trans). 1,3-
Diethylphthalat*
Dimethoxybenzldrne. 3.3'-
Dlmethylphenol. 2.4-
Dimethylphlhalate
Di-n-butylphthalate
DInHrotofuene. 2.6-
Dinttro-2-meltiytphenol, 4.6-
Dlnitrophenot. 2.4-
Dinltrotoluene 2 4
Dioxane. 1.4-
Di(n)octyl phthalale
D. 2,4-
Ethyl methacrylale
Ethyttxruane
Ethylene dibromide
Ethylene oxide
Ethylene thlourea
Fluoranthena
Fluorene
Formaldehyde
Furfural
H^ptachlor
Heptachlorobiphenyl
Hexachlorobenzene
Hexachloroblphenyl
Hexachlorobutadiene
Hexachlorocyclohexane. gamma (Lindane)
Hexachlorocyclopentadiene
Hexachloroethane
Hexachlorophene
Hexanone, 2-
lndeno(1.2.3-cd)pyren«
Isophorone
Maleic hydrajida
Methoxychlor
Methyl t butyl ether
Methyl 2 Pentanone 4 (MIBK)
Methylene chloride
Methylnaphthalene. 2
Monochlorobiphenyl
Naphthalene
Nitroanihne 2
Nitioaniline 3
Inhalation
Slope
Factor
(mg/kg d)A-1
NA
NA
9 1E 02
1 2E«00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
4 5E-02
NA
45E+00
NA
1 6E+00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
0 75
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg d)
1 4E 02
36E 02
NA
2 3E 03
50E 03
75E 04
2 9E 04
1 4E-03
1 4E 03
20E01
NA
50E-03
NA
2 5E-02
25E-04
NF
50E 04
50E-04
NA
50E 03
25E 03
23E 02
7 IE 02
1 4E 05
NA
20E 05
1 OE 02
1 OE 02
50E 02
36E 03
1 3E 04
NA
20E-04
NA
50E 05
75E 05
50E 06
25E 04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
tJF
NA
1 OE 02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E-04
3E-05
3E-05
3E 05
3E 05
55E 06
3E-05
3E05
3E 05
7E-05
2E-04
55E-06
55E06
1 6E 05
55E 06
55E 06
55E 06
55E-06
4 9E 04
55E-06
39E 05
25E 04
50E 04
1 2E 04
3 1E 05
15E 10
55E 06
67E 06
6 IE 04
55E 06
55E 07
1 4E 08
55E 06
1 4E 08
1 OE 04
55E 05
55E 06
55E-06
32E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
4 2E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
N1 avg
Nt avg
Nt avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
•
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Ml avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Nt avg
N1 avg
N1 avg
HI avg
N1 avg
Nl avg
Nt avg
Nl avg
Ml avg
Nt avg
Nl avg
Nl avg
Nt avg
m avg
Nl avg
Adult
Cancer
Risk
NT
NT
56E-12
74E-11
NT
NT
NT
80E-12
80E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
43E 10
53E 11
NT
NT
NT
1 3E 10
NT
1 2E-11
NT
44E-11
NT
39E-11
NT
NT
38E 13
NT
NT
NT
NT
NT
NT
NT
NT
32E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
1 4E 11
1 BE 10
NT
NT
NT
20E 11
20E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 09
1 3E 10
NT
NT
NT
34E-10
NT
30E-11
NT
1 1E-10
NT
97E-11
NT
NT
95E-13
NT
NT
NT
NT
NT
NT
NT
NT
80E 12
NT
NT
fJT
NT
NT
School age
Cancer
Risk
NT
NT
84E-12
1 1E-10
NT
NT
NT
1 2E 11
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
65E 10
79E-11
NT
NT
NT
20E 10
NT
1 8E-11
NT
66E-11
NT
58E-11
NT
NT
57E-13
NT
NT
NT
NT
NT
NT
m
Nt
48F 12
NT
NT
lit
(IT
HI
Faimer
Cancel
Risk
NT
NT
1 2E-11
1 6E-IO
NT
NT
1 8E-11
1 8E-11
NT
NT
NT
NT
NT
NT
it i
NT
NT
NT
NT
NT
NT
NT
NT
96E-10
1 2E-10
NT
NT
NT
30E-10
NT
2 7E-11
NT
9 7E-11
NT
86E-11
NT
NT
84E-13
NT
NT
NT
NT
NT
tIT
NT
tIT
7 IE 12
NT
NT
fJT
nr
NT
                                                                                                                                                Adult      Child   School age   Farmer
                                                                                                                                             Noncancer Noncancer Noncancer  Noncancer
                                                                                                                                                HQ       HO       HQ        HQ
66E-07
1 3E-08
NT
2 IE 07
96E-08
2 BE 07
1 7E-06
3 4E-07
34E-07
32E-09
NT
42E-08
NT
2 4E-OB
8 4E-07
NT
4 2E-07
4 2E-07
NT
4 2E 08
60E-07
42E 07
2 7E-07
3 1E-04
NT
28E 10
2 IE 08
2 6E-OB
4 7E-07
59E 08
1 7E-07
NT
1 1E-06
NT
77E-05
28E 05
42E05
84E-07
1 6E-05
NT
NT
5 IE 09
35E 08
1 7E 08
22E 09
84E 08
7 IF -08
NT
NT
2 IF 08
1 BF OS
NT
25E 06
50E 08
NT
80E 07
36E-07
1 IE 06
63E-06
1 3E-06
1 3E-06
1 2E-08
NT
1 6E-07
NT
90E 08
32E06
NT
1 6E 06
16E-06
NT
1 6E-07
22E06
1 6E 06
IDE 06
1 2E-03
NT
1 OE 09
79E 08
96E 08
1 7E 06
22E-07
63E-07
NT
39E-06
NT
29E04
1 OE 04
16E 04
32E 06
6 IE-OS
NT
NT
1 9E 08
1 3E 07
6 3E 08
8 4E 09
3 IE 07
2r,F 07
tJT
NT
7 9F 08
6 n Or>
NT
1 5E 06
30E-08
NT
48E 07
2 2E-07
63E-07
3 BE 06
76E 07
76E-07
73E-09
NT
9 5E-08
NT
54E 08
1 9E-06
NT
95E-07
95E-07
NT
95E-08
1 3E-06
94E-07
60E-07
70E 04
NT
63E 10
48E 08
5 BE -08
1 IE -06
1 3E 07
3 BE 07
NT
24E 06
NT
1 7E 04
63E-05
95E 05
1 9E 06
3 7E-05
NT
NT
1 2E 08
80E 08
38E 08
^ IE 09
1 9F 07
1 r,F -07
NT
tJT
48F 08
4 IF. 05
111
66E-07
1 3E-08
NT
2 IE 07
96E 08
2 BE 07
1 7E-06
34E-07
34E 07
3 2E-09
NT
4 2E-OB
NT
24E 08
84E-07
NT
42E 07
42E 07
NT
4 2E 08
60E 07
42E 07
2 7E-07
3 IE 04
NT
2 BE 10
2 IE 08
26E-08
4 7E-07
S9E 08
1 7E 07
NT
1 IE -06
NT
77E05
2 BE 05
4 2E-05
84E 07
1 6E-05
NT
NT
5 IE 09
35E 08
1 7E 08
22E 09
84E 08
7 IF 08
NT
NT
2 IE 08
1 BF 01
NT
Volume V Appendix V
-------
TABLE 11  Average l\    ./on Risks and Noncancer HQs in Subaica W2
CHEMICAL
Acenaphthane
Acenaphthylene
Acetaldehyde
Acetone
Acelopherone
Acrylonrtrlle
Anthracene
Benzene
Benzole acid
Benzotrichloride
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)Duoranthene
nenzo(g.h.l)perytene
Benzo(k)fluoranthene
Bls(2-chloroethoxy) methane
Bis(2-chloroethyl)ether
Bls(2-chloroisopropyl)ettier
Bij(2-ethylhexyl)ph(halate
Bromodichloromethane
Bromoform
Bromomethane
Bromodiphenyt ether, p-
Butanone, 2- (Methyl ethyl ketone)
Butyl be nrytphthilate
Carbon dlsuffide
Carbon tetrachlorlde
Chlordane
Chtero-3-methylphenol, 4-
Chloroanlllne. p- (4-Chtoroaniline)
Chlorobenzene
Chlorobenzllate
Chloroethane (Ethyl chloride)
Chloroform
Chlotomethane
Chtoronaphthalene. beta
Chlorophenol. 2-
Chlorodlphenyl ether. 4- ,
"hryjene
>esol. m-
:t»sol. o- (2-Methylphenol)
>esol. p-
^rotonaldehyde
"umene
)DE, 4,4'-
)ibenz(a.h)anthracene
?ibromochloromethana
)ichlorobenzene, 1 .3-
)ichlorobenzene. 1.4-
)ichlorobenzene, 1.2-
)ichlorobenzidine. 3.3'-
)ichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)A-1
NA
NF
77E^)3
NA
NA
2 4E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
27E-01
NA
6 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0 004375
NF
NA
0 04375
004375
0 004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RfD
(mg/kg-d)
1 5E-02
NF
6 4E 04
25E 02
25E 02
1 4E 04
7 5E-02
43E-04
1 OE»00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E-03
50E 03
50E 03
36E-04
NA
7 IE 02
50E 02
7 1E 04
1 41 04
15E-05
NF
1 OE 03
1 4E 03
50E-03
7 IE 01
2 5E 03
NA
20E02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
6 4E-04
NA
NA
50E-03
NA
5 7E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E 06
67E-06
3 OE 04
2 9E 03
2 9E 04
20E^>4
55E-06
, 1 5E-05
1 1E-05
32E-05
55E-06
55E 06
55E-06
55E 06
55E 08
67E-06
1 3E-05
6 7E 06
37E-05
1 OE 04
55E-06
4 9E-04
6 7E-06
5 IE 05
55E 06
89E-05
1 6E 04
5 5E-07
67E-06
67E06
55E-06
3 7E-05
4 9E 04
2 7E 04
25E 04
67E-08
55E06
67E06
55E06
55E06
55E-06
55E 06
1 4E 04
55E 06
55E 07
55E 06
2 6E-05
55E-06
55E 06
5 5E 06
33E 05
4 7E-08
Subarea
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 avg
W2avg
W2avg
W2avg
W2 avg
Ofl-site
Vapor
Cone
(ug/m3)
64E 07
6 4E 07
2 9E 05
2 BE 04
2 BE -05
1 9E-05
5 3E 07
1 4E 06
1 IE 06
31E-06
5 3E 07
5 3E 07
5 3E-07
53E07
53E 07
64E-07
1 3E 06
8 4E 07
36E 06
99E 06
5 3E-07
47E 05
6 4E 07
49E-06
53E 07
86E 06
1 5E-05
5 3E-08
84E07
6 4E-07
5 3E 07
35E06
4 7E-05
2 6E 05
2 4E 05
6 4E-07
5 3E-07
64E07
53E07
5 3E 07
53E07
53E 07
1 3E 05
53E 07
53E 08
53E 07
2 SE 06
53E 07
53E07
53E 07
32E 06
4 5E 09
Cancer
Adult
Dose
(mg/kg-d)
23E-11
23E 11
1 OE 09
9 BE 09
99E 10
68E-10
1 9E-11
50E-11
38E-11
1E-10
9E-11
9E-11
9E-11
9E-11
9E-11
23E 11
45E 11
23E-11
1 3E-10
35E-10
1 9E-11
1 7E-09
23E-11
1 7E-10
1 9E-11
30E-10
54E-10
1 9E-12
23E-11
23E-11
1 9E-11
1 2E-10
1 7E-09
90E-10
83E-10
23E-11
1 9E-11
23E 11
9E-11
9E-11
9E-11
9E 11
7E 10
9E tl
9E 12
9E 11
9E 11
9E 11
9E 11
9E 11
IE 10
6E 13
Cancer
Child
Dose
(mg/kg-d)
56E 11
56E 11
2 5E 09
24E 08
2 5E 09
1 7E 09
46E-11
1 2E-10
95E-11
27E 10
46E-11
46E-11
46E-11
46E-11
46E-11
56E-11
1 1E-10
56E-11
3 1E-10
8 7E-10
46E-11
4 1E-09
56E-11
43E-10
46E-11
75E-10
1 3E-09
46E-12
56E-11
56E-11
46E-11
31E-10
4 1E-09
2 2E-09
2 IE 09
56E-11
46E-11
56E 11
46E-11
46E-11
46E 11
46E 11
1 2E 09
46E 11
46E 12
46E 11
2 2E 10
46E 11
46E 11
46E 11
28E 10
39E 13
Cancer
School-age
Dose
(mg/kg-d)
34E-11
34E-11
1 5E-09
1 5E 08
1 5E-09
1 OE-09
28E-11
75E-11
S8E-11
16E-10
28E 11
28E-11
28E-11
28E-11
28E-11
34E-11
68E-11
34E 11
1 9E-10
52E-10
2BE-11
25E-09
34E-11
26E-10
28E-11
45E-10
81E-10
28E 12
34E-11
34E-11
28E-11
1 9E-10
25E-09
1 4E-09
1 2E-09
34E-11
28E-11
34E-11
28E-11
28E-11
28E-11
28E-11
7 IE 10
2 BE 11
2 BE 12
2 BE 11
1 3E 10
2 BE 11
2 BE 11
2 BE 11
1 7E 10
2 4E 13
Cancer
Farmer
Dose
(mg/kgd)
50E 11
50E 11
2 3E 09
2 2E 08
22E-09
1 5E 09
41E-11
1 1E-10
85E-11
24E-10
41E-11
41E-11
41E-11
4 IE 11
41E-11
50E-11
1 OE-10
50E-11
28E-10
7 7E-10
41E-11
37E-09
50E-11
39E-10
41E-11
67E-10
1 2E-09
4 1E 12
50E-11
50E 11
41E-11
2BE-10
37E09
20E09
1 8E-09
50E-11
4 1E-11
50E-11
41E-11
41E-11
4 IE 11
4 1E-11
1 OE 09
4 IE 11
4 1E 12
4 IE 11
20E 10
4 IE 11
4 IE 11
4 IE 11
25E 10
35F 11
Noncancer
Adult
Dose
(mg/kgd)
1 BE-10
1 8E-10
79E-09
7 6E-08
7 7E-09
53E-09
1 4E 10
39E-10
3 OE-10
84E-10
1 4E-10
1 4E 10
1 4E-10
1 4E-10
1 4E 10
1 8E-10
35E-10
1 BE- 10
98E-10
27E4»
1 4E-10
1 3E-08
1 8E-10
14E-09
1 4E 10
23E^»
42E-09
1 4E-11
1 8E-10
1 8E 10
1 4E-10
97E-10
1 3E-08
70E09
64E-09
1 BE 10
1 4E-10
1 BE 10
1 4E-10
1 4E-10
1 4E-10
1 4E-10
37E09
1 4E 10
1 4E 11
1 4E 10
69E 10
1 4E 10
1 4E 10
1 4E 10
8 BE 10
1 ?E 12
Noncancer
Child
Dose
(mg/kg-d)
66E-10
66E 10
3 OE 08
2 BE 07
2 9E-08
2 OE 08
54E 10
1 4E-09
1 1E-09
31E-09
54E-10
54E-10
54E-10
54E-10
54E 10
66E-10
1 3E-09
66E-10
37E-09
1 OE 08
54E-10
48E-08
66E 10
5 IE 09
S4E-10
88EO«
t 6E-08
54E-11
66E-10
66E-10
54E 10
36E09
4 BE 08
26E08
24E 08
66E-10
54E 10
66E 10
54E-10
54E 10
54E 10
54E 10
1 4E 08
54E 10
54E 11
54E 10
2 RE 09
54E 10
54E 10
54F. 10
3 3E 09
4fiF 12
\loncancer
School-age
Dose
(mg/kg-d)
4 OE-10
40E 10
1 BE 08
1 7E^)7
1 7E 08
1 2E-06
33E-10
87E-10
67E-10
19E09
33E-10
33E-10
33E-10
33E-10
33E-10
4 OE-10
79E-10
40E 10
2 2E 09
6 IE 09
33E-10
2 9E-08
40E 10
31E^)9
33E 10
53E09
94E 09
33E-11
4 OE-10
40E 10
33E-10
22E09
2 9E 08
1 6E 08
1 5E 08
4 OE-10
33E 10
40E 10
33E 10
33E 10
33E 10
33E 10
83E 09
33E 10
33E 11
33E 10
1 6E 09
33E 10
33E 10
33E 10
20E 09
2BF 12
Moncancer
Farmer
Dose
(mg/kg d)
1 BE 10
1 BE 10
7 9E 09
7 6E 08
7 7E 09
5 3E 09
1 4E 10
39E 10
30E-10
84E 10
14E 10
14E 10
1 4E-10
14E 10
1 4E 10
18E-10
35E 10
1BE 10
9 BE 10
27E09
1 4E-10
1 3E 08
18E 10
1 4E 09
14E 10
23E09
42E-09
14E-11
1 8E-10
1 BE 10
14E-10
97E-10
1 3E-08
70E09
84E09
18E 10
1 4E-10
1 BE 10
1 4E-10
1 4E-10
ME 10
1 4E 10
37E09
1 4E 10
1 4E 11
1 4E 10
69E 10
1 4E 10
1 4E 10
1 4E 10
8 BE 10
1 2E 12
 olume V. Appendix V 14
-------
TABLE 10  Average Inhalation Risks and Noncancei HQi in Subarra W 1
CHEMICAL
1,2.3.789 HxCDF
1 2.3 4.6.7.8 HpCDF
1.2.3.4. 7.8.9 HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trlvalenl)
Copper
Laid
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
-) Total nitrogen oxides (NOx)
4 ToUl sulfur oxides (SOx)
1 3srtlculate matter
^esplreble pattictlates
Inhalation
Slope
Factor
(mg/kg d)"-1
1 5E»04
1 5E»03
1 5E»03
1 5E»02

NA
NA
SO
NA
64
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E05
36E-05
1 3E-03
13E 04
1 3E 03
25E-01
NA
NA
2 IE 05
50E03
1 3E 03
1 3£ 03
1 8E 05
7 5E 02
50E-04
NA
NA
NA
NF
Emission
Rale
(g'sec)
293E-10
930E 09
1 22E 09
1 89E 08
4 28E 08
24E04
42E06
37E05
15E04
33E08
16E-05
7 IE 07
7 1E 07
94E-05
43E 05
1 4E-03
50E 06
4 7E 04
1 5E 05
34E 05
1 2E 04
32E-02
24E+00
9 IE 02
7 2E 02
7 2E-02
Subarea
Wl avg
Wl avg
W1 avg
W1 avg

W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
Wl avg
W1 avg
Wl avg
W1 avg
Wl avg
W1 avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
Adult
Cancef
Risk
3 1E-11
9 BE 11
1 3E 11
20E 11
99E-10
NT
NT
1 3E-08
NT
20E-12
69E-10
20E-10
NT
NT
NT
NT
30E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
7 7E 11
24E 10
32E II
50E 11
25E 09
NT
NT
32E-08
NT
49E-12
1 7E 09
51E-10
NT
NT
NT
NT
74E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
47E 11
1 5E 10
1 9E 11
30E 11
1 5E 09
NT
NT
20E08
NT
29E 12
10E09
31E-10
NT
NT
NT
NT
45E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
69E 11
22E 10
29E 11
44E 11
22E 09
NT
NT
29E-08
NT
43E-12
1 5E 09
46E-10
NT
NT
NT
NT
66E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                              Adult      Child    School age   Farmer
                                                                                                                                            Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                               HQ        HO        HQ       HO
NT
NT
NT
NT
NT
NT
23E-06
2 7E 05
2 3E 04
14E09
70E06
3 IE-OS
1 6E-10
NT
NT
36E-03
55E08
21E4»
66E^>7
1 IE 04
88EX)8
35E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
B6E-06
t OE 04
66E04
S4E09
26E-05
1 2E-07
58E-10
NT
NT
t 3E 02
20E07
77E05
25E06
40E-04
33E^)7
1 3E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
52E06
6 1E-05
5 2E 04
33E-09
1 6E-05
7 OE 08
35E-10
NT
NT
8 IE 03
1 2E 07
4 7E 05
1 5E 06
24E 04
20E 07
79E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
23E06
27E05
2 3E 04
1 4E 09
70E^)6
3 IE 08
1 6E-10
NT
NT
36E^)3
55Efl8
2 IE 05
66E07
1 1EO4
88E^»8
35E^)3
NT
NT
NT
NT
                                                                               Total Risk   22E-08    5 5E-08    3 3E-08    4 9E-08
                                                                                                                                    Total HI   85E-03   3 2E 02    1 9E 02    8 5E 03
  NA - Not applicable
  NF - Not found
  NT = No toxicrty Information
  HQ • Hazard quotient
  HI - Hazard index
  nlume V Appendu V -
-------
  TABLE 4 Averaged      Vi Risks and Noncancei HQs in Subaroa Nl
  CHEMICAL

  Nrtroaniline, 4-
  Nitrobenzene
  Nrtrophenol. 2-
  Nitrophanol, 4-
  N Nrtrojo-dl n-butylamlne
  N-NKrno-dl-n-propylamin*
  N-Nttrosodlphanvtamlne (Diphenylamine)
  Nofiachloroblphanyl
  Ocfachloroblphenyi
  Pantachlorobenzen*
  P«nt*cMoroblph«nv1
  PantachlotonHrob«nzan«
  Pentachlorophanol
  Phananthrena
  Phenol
  Pyrena
  Safrole (5-(2-Propenyt)-1,3-beruodioxole)
 Stytana
 Tatrachlofobiphanyt
 Tatrachkxocthana. 1.1.1.2-
 Tetrachloroethane. 1.1.2.2
 Tatrachloroalhana
 Tetrachlofophanol. 2,3.4.6
 Toluene
 Tiichloro-1.2,2-trrfluoro«thine. 1.1.2-
 Trlchlorob«nzene. 1.2.4-
 Trichloroblphanyt
 Trichloroelhana. 1.1.1- (Methyl chloroform)
 Trichloroethane. 1,1.2-
 Trtchloroattiana
 Trlchlorofluoromethane
 Trichlotophenol. 2.4.5-
 Trlchlorophenol. 2.4.6-
 Vtnyl acetate
 vinyl chloride
 Xylana, m/p- (m/p-D)methyl benzene)
 Xytene, o- (o-Dimathyl benzene)
2.3.7,e-TCDO
1.2.3,7.8-PCDO
1.2.3.4.7.8-HxCDO
1.2.3.6.7.8-HxCDO
1.2.3,7.B.9HxCDO
1.2.3.4.6.7.8-HpCDD
OCDD
2.3.7.8TCDF
1.2.3.7.8PCDF
2.3.4.7.8 PCDF
1.2.3.4.7.8 HxCDF
1.2.3.6.7.8 HxCDF
2.3.46.7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)«-
NF
NA
NF
NF
54E*00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
15E+05
75E404
1 5E+04
1 5E»04
1 5E+04
1 5E+03
1 5E*02
1 5E»04
75E»03
75E*04
1 5E*04
1 5E*04
1 5E*04
RAC
1 (mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
002625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7SE-04
75E-03
NA
ISE-Ot
75E-03
NF
7 1E-02
NA
75E-03
NA
2 5E 03
2 BE -02
2 1E*00
1 4E-02
NA
7 1E4J2
1 OE-03
NA
5 OE-02
25E-02
NA
14E-02
NA
50E01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E-06
55E-06
1 2E-04
67E-06
67E-06
14E08
1 1 4E-08
4 BE -05
1 4E-08
34E-OS
55E-06
87E-06
55E-06
55E-06
1 2E-04
23E-05
I4E-08
55E-06
51E05
6 BE -06
33E-04
55E-06
30E-OB
1 3E-05
1 3E-05
1 9E-05
2 5E 04
S5E-06
55E-06
64E-05
2 5E-04
3 BE -04
55E-06
108E-11
678E-11
895E-11
t 66E-10
1 09E-10
1 24E 09
6 15E 09
8 77E 11
345E-10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
N1 avg
Nl avg
Nt avg
Nt avg
Nl avg
Nl avg
Nt avg
Nl avg
Nl avg
Nl avg
Nlavg
Nl avg
Nlavg
Nlavg
Nl avg
Nl avg
Nlavg
Nl avg
Nl avg
Nl avg
Nt avg
N1 avg
Nt avg
Nl avg
Nl avg
Nl avg
Nt avg
Nt avg
Nt avg
Nt avg
Nlavg
Nt avg
Nt avg
Nl avg
Nl avg
Nlavg
Nl avg
Nl avg
N1 avg
Nt vg
Nl vg
N1 vg
Nl vg
Nl vg
Nl vg
Nl vg
Nt avg
Nl avg
Nl avg
Ml avg
Ofl-sile
Vapor
Cone
(ug/m3)
9 4E-07
7 7E-07
94E 07
7 7E 07
1 7E 05
94E-07
9 4E-07
20E-09
20E09
67E-06
20E09
47E-06
7 7E-07
9 4E-07
7 7E 07
7 7E 07
32E-06
20E-09
7 7E 07
7 7E-07
72E-06
9 5E-07
86E05
46E05
7 7E-07
42E09
t BE -06
18E-06
26E-06
3 4E-05
7 7E 07
7 7E-07
9 OE 06
34E-05
5 3E 05
7 7E 07
15E-12
95E-12
t 3E 11
23E 11
1 5E 11
t 7E 10
86E 10
1 2E 11
4 BE 11
6SE 11
20E 10
1 9E 10
2 1E-10
Cancer
Adult
Dose
(mg/kg-d)
33E-11
27E-11
33E-11
27E 11
60E-10
33E-11
33E-11
69E 14
69E-14
23E-10
69E-14
1 7E 10
27E-11
33E-11
27E-11
27E-11
5 7E-10
1 1E-10
69E-14
27E-11
27E-11
25E-10
34E-11
30EX)9
16E-09
27E-11
1 5E-13
62E-11
62E-1I
92E-11
27E-11
27E It
32E 10
12E-09
1 9E-09
27E-11
53E 17
33E-16
44E 16
82E 16
54E 16
6 IE 15
30E 14
43E 16
1 7E 15
23E 15
70E 15
66E 15
74E 15
Cancer
Child
Dose
(mg/kg-d)
82E 11
6 BE 11
B2E-11
6 BE 11
1 5E-09
82E-11
82E-11
1 7E-13
1 7E-13
58E-10
1 7E-13
41E-10
68E-11
82E-11
68E-11
68E-11
1 4E-09
28E-10
1 7E-13
68E-11
68E-11
63E-10
84E-11
75E-09
41E-09
68E-11
37E-I3
1 5E-10
15E-10
23E-10
30E-09
68E-11
68E-11
79E-10
30E09
47E-09
68E-11
13E 16
B3E 16
1 IE 15
20E 15
1 3E 15
1 5E 14
75E 14
1 IE 15
42E 15
57E 15
1 BE 14
1 6E 14
1 BE 14
Cancer
School-age
Dose
(mg/kg-d)
50E-11
41E 11
50E 11
41E-11
90E-10
50E 11
50E-11
1 OE-13
1 OE-13
35E-10
1 OE-13
25E-10
41E-11
50E-11
41E-11
4 IE-It
85E-10
1 7E-10
1 OE-13
41E-11
41E-11
36E-10
50E-11
45E-09
24E-09
4 IE 11
2 26-13
93E-11
93E-11
1 4E-10
18E-09
41E-11
4 1E-11
4 8E-10
18E-09
2 BE 49
4 IE-It
80E 17
50E 16
66E-16
1 2E 15
B IE 16
92E 15
46E 14
65E 16
26E 15
35E 15
1 IE 14
99E 15
1 IE 14
Cancer
Farmer
Dose
(mg/kg-d)
73E-11
60E 11
73E-11
60E 11
1 3E-09
73E-11
73E 11
1 5E-13
1 5E-13
52E-10
1 5E-13
37E-10
60E-11
73E 11
60E-11
60E-11
1 3E-09
25E 10
1 5E 13
80E-11
60E-11
56E-10
74E-11
67E09
36E-09
60E-11
33E 13
1 4E-10
1 4E 10
20E-10
27E-09
60E-11
60E-11
70E-10
27E09
42E09
60E-11
1 2E 16
74E 16
98E-16
18E 15
1 2E 15
1 4E 14
6 7E 14
96E 16
3 BE 15
1 6E 14
1 5E 14
1 BE 14
Noncancer
Adult
Dose
(mg/kg-d)
26E-10
2 1E-10
26E 10
2 IE 10
4 6E-09
26E-10
26E-10
54E-13
54E-13
1 8E-09
54E-13
13E09
2 1E-10
26E-10
2 1E-10
21E10
44E-09
86E-10
54E-13
21E-10
2 IE 10
20E-09
26E-10
23E-08
1 3E-08
21E-10
1 2E-12
48E-10
4 BE 10
71E-10
94E-09
21E-10
2 IE 10
94EO9
15E-08
2 IE 10
41E-16
26E t5
34E 15
63E 15
42E 15
48E 14
24E 13
34E 15
1 3E 14
18E 14
55E 14
5 IE 14
5 BE 14
Noncancer
Child
Dose
(mg/kg-d)
96E-10
79E-10
96E-10
79E-10
1 7E-08
96E-10
96E-10
20E-12
20E-12
6 BE -09
20E 12
4 BE 09
79E-10
98E-10
79E-10
79E 10
1 6E-08
32E09
20E-12
79E-10
79E-10
73E-09
97E-10
8 BE 08
4 7E-08
79E-10
43E-12
1 BE -09
18E-09
27E-09
3 5E-08
79E-10
79E-10
92E-09
3 5E-08
54E08
79E-10
15E 15
97E 15
1 3E 14
24E 14
t 6E 14
t BE 13
8 BE 13
1 3E 14
49E 14
6 7E 14
20E 13
1 9E 13
2?E 13
Noncancer
School-age
Dose
(mg/kg-d)
5 BE 10
48E-10
58E-10
48E-10
1 OE 08
58E-10
58E-10
1 2E-12
12E 12
4 1E-09
12E 12
29E09
4 BE 10
58E 10
48E-10
48E-10
1 OE 08
19E-09
1 2E 12
48E-10
4 8E-10
44E49
59E 10
2 9E 08
48E 10
26E 12
1 1E 09
1 IE 09
16E-09
2 IE 08
4 BE 10
4 BE 10
56E09
21E08
3 3E 08
48E-10
94E 16
59E 15
77E 15
14E 14
94E 15
t IE 13
53E 13
" 76E 15
30E 14
40E 14
1 2E 13
1 2E t3
1 3E 13
Noncancer
Farmer
Dose
(mg/kg-d)
26E 10
21E-10
26E-10
21E-10
46E09
26E-10
26E-10
54E 13
54E-13
1BE09
54E 13
1 3E-09
2 IE 10
26E-10
21E-10
21E-10
44E09
86E-10
54E-13
2 IE 10
2 IE 10
20E-09
26E-10
2 3E-OB
1 3E-08
2 IE-ID
1 2E 12
4 BE 10
48E-10
7 IE 10
9 4E 09
2 IE 10
2 IE 10
25E09
94E09
1 5E-08
2 1E-10
4 IE 16
26E 15
34E 15
63E 15
42E 15
4 BE 14
24E 13
34E 15
1 3E 14
18E 14
55E 14
5 IE 14
5 BE 14
/oil/me V. Appendix v-14
-------
TABLE 4  Average Inhafalion Risks and Noncancei MOs in Subatra Nl
CHEMICAL
Nitroaniline. 4-
Nitrobenzene
Nrtrophenol. 2-
Nrt/ophenol. 4-
N Nitroso di n butylamine
N Nrtooso-di-ivpiopylamine
N Nrttosodiphenytamine (Diphenylamine)
Nonachlorobiphenyl
Octachlofoblphenyl
Pentachlotobcnzene
Pentachloroblphenyl
Pentachloronrtrobenzene
Pentaehlorophanol
"henanttvene
Phenol
f*yien«
Safrole (5-(2-Piop»ny1)-1.3 benzodioxole)
Styrene
tetrachloroblphenyl
lebachloroethane. 1.1 1.2-
lebachtoroalhane. 1.1.2.2-
fetrachloiMthene
retrachloiophenol. 2.3.4.6
Toluene
rrlchloio-1.2,2-lrrnuoioethane. 1.1.2-
'nchlotoberuene, 1,2.4-
richljtobiphonyl
rlchlofoethane, 1.1.1- (Methyl chloroform)
richtoioethane, 1,1.2-
rlchloroethene
tichlorofluoiomethane
nchlorophenol. 2.4.5-
rlchlorophenol, 2,4.6-
'inyl acetate
Inyl Chloride
ylene, m/p- (m/p Dimethyl benzene)
ylene, o- (o Dimethyl benzene)
V
.3.7.8 TCDD
.2.3.7.8PCDO
2.3,4.7,8 HxCDO
236.78HxCDD
.2 3 789 HxCDD
.2.3,4.6.7 BHpCOO
COD
3.7,8 TCDF
2.3 7 8 PCDF
3.4,7 8 PCDF
23478 HxCDF
2 3 6 7.8 HxCDF
3 4 6 7,8 H«CDF
Inhalation
Slope
F actoi
(mg/kgd)"-1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E^>2
20E-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
6 OE 03
NA
NA
1 OE-02
NA
30E-01
NA
NA

1 5E»05
7 5E+04
1 5E»04
1 5E»04
1 5E»04
1 5E«03
1 5E»02
1 5E*04
75E*03
7 5E«04
1 5E'04
1 5E«04
1 5E»D4
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E^)4
75E 03
NA
1 5E-01
75E-03
NF
7 IE 02
NA
75E-03
NA
25E^)3
75EXJ3
2 9E-02
2 1E+00
1 4E 02
NA
7 1E 02
1 OE-03
NA
50E 02
2 5E-02
NA
1 4E 02
NA
50E-01
5 OE-01

NA
NA
NA
NA
NA
tIA
NA
NA
HA
NA
HA
NA
NA
Emission
Rate
(a/sec)
67E 06
5 5E 06
67E 06
55E 06
1 2E-04
6 7E-06
67E-06
1 4E-08
1 4E-08
4 8E-05
1 4E-08
34E-05
55E-06
67E-06
55E06
55E-06
1 2E-04
2 3E-05
1 4E-08
55E 06
55E 06
5 IE 05
68E 06
6 IE 04
33E 04
55E-06
3 OE 08
1 3E 05
1 3E 05
1 9E 05
25E 04
5 5E 06
55E-06
6 4E 05
2 5E 04
38E 04
55E-06

1 08E 11
6 78E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
3 45E 10
467E 10
1 43E 09
1 33E 09
t 50E 09
Subarea
N1 avg
N1 avg
Nl avg
N1 avg
Nt avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
N1 avg
Nl avg
Nl avg
Nt avg
N1 avg
N1 avg
Nt avg
Nl avg
Nt avg
N1 avg
Nl avg
Nl avg
Nt avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
Nt avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
Nl avg

Nl avg
Nl avg
Nl avg
Nl avg
Nl avg
Nt avg
Nl avg
Nt avg
Nl avg
III avg
Nl avg
fll avg
Ml avg
Adult
Cancer
RisK
NT
NT
NT
NT
32E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E 13
55E 12
5 1E-13
NT
NT
NT
NT
NT
NT
35E 12
55E 13
NT
NT
2 7E-13
NT
36E-10
NT
NT

80E 12
25E 11
66E 12
1 2E 11
8 IE 12
92E 12
45E 12
65E 1?
1 3E 11
1 7E 10
1 1E 10
99E It
1 IE 10
Child
Cancer
Risk
NT
NT
NT
NT
80E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 12
1 4E 11
1 3E-12
NT
NT
NT
NT
NT
NT
B7E 12
1 4E-12
NT
NT
6BE-13
NT
90E-10
NT
NT

20E 11
62E 11
1 6E 11
3 IE 11
20E 11
2 3E 11
1 IE II
1 6E 11
3 2E 11
4 3E 10
26E 10
2 5E 10
?8E 10
School age
Cancer
Risk
NT
NT
NT
NT
4 BE 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-12
83E-12
77E-13
NT
NT
NT
NT
NT
NT
53E-12
82E-13
NT
NT
41E-13
NT
55E-10
NT
NT

1 2E 11
3 BE 11
1 OE 11
1 8E 11
1 2E 11
1 4E 11
68E 12
98E 12
1 9E 11
26E 10
1 6E 10
1 5E 10
1 7F 10
Faimei
Cancer
Risk
NT
NT
NT
NT
72E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-12
12E 11
1 1E-12
NT
NT
NT
NT
NT
NT
7 BE 12
1 2E-12
NT
NT
60E-13
NT
8 1E-10
NT
NT

1 8E-11
56E It
1 5E 11
2 7E It
18E 11
20E 11
1 OE 11
1 4E It
2SE 11
38f 10
7 3r 1C)
2 ?! 10
? M 10
                                                                                                                                              Adult      Child    School age  Farmer
                                                                                                                                            Noncancer Noncancer Noncancer Noncancer
                                                                                                                                               HO       HQ        HQ        HQ
NT
1 5E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-06
2 8E 08
NT
14E-09
2 8E 08
NT
1 2E-08
NT
2 BE 08
NT
79E^)7
3 5E 08
82E-07
59E-09
1 5E-08
NT
67E 09
4 BE -07
NT
1 9E 07
84E-09
NT
1 7E-07
NT
29E-08
42E-10
NT
NT
NT
NT
NT
NT
NT
nr
NT
HI
m
Nl
III
NT
55E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E06
1 1E-07
NT
53E09
1 1E-07
NT
4 5E-08
NT
1 1E-07
NT
29E 06
1 3E 07
3 IE 06
22E08
55E08
NT
25E 08
1BE06
NT
70E 07
32E 08
NT
64E 07
NT
1 IE 07
1 6E 09
NT
Nt
NT
Nl
Nt
Nt
III
HI
Nl
III
nr
in
in
NT
33E06
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E-06
63E-08
NT
32E^)9
63E-08
NT
2 7E-08
NT
63E-08
NT
16E 06
78E^)8
1 9E 06
1 3E4>8
3 3E 08
NT
1 5E 08
1 1E«6
NT
42E 07
1 9E 08
NT
39E 07
NT
66E 08
95E-10
tlT
Nl
NT
NT
Nt
lit
Nl
Nt
HI
lit
HI
HI
111
NT
1 5E 06
Nl
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 06
2 BE -08
NT
1 4E 09
2 BE -08
NT
1 2E 08
NT
28E^»
NT
7 9E 07
35E 08
8 2E 07
59E 09
1 5E 08
NT
67E 09
4 BE 07
NT
1 9E 07
84E 09
NT
1 7E 07
NT
2 9E 08
42E 10
NT
NT
Nl
NT
NT
Nt
NT
Nl
Nt
tit
Nt
fit
HI
  >lume V. Appendix V
-------
TABLE 4  Average lnK    jn Risks and Noncancer HQs in Subarea N1
CHEMICAL
1.2.37.8.9 HxCDF
1. 2.3.4.6.7.8 HpCDF
1,2.3.4.7,8,9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivalent)
CoDDer
ww^f *»1
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nHiogen oxides (NOx)
Total sulfur oxides (SOx)
Particulate matter
Resplrable particulars
Inhalation
Slope
Factor
(mg/kg-d)*- 1
1 5E*04
1 5E«03
1 5E»03
1 5E»02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA •'
NA

NA
000035
0000263
0000125
0 004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E-05
36E-05
1 3E-03
1 3E-04
1 3E-03
25E-01
NA
NA
2 IE 05
50E-03
1 3E-03
1 3E-03
1 BE 05
7 5E-02
50E-04
MA
NA
NA
NF
Emission
Rale
(g/sec)
293E 10
930E09
1 22E 09
1 B9E 08
4 28E-08
, 2 4E-04
42E-06
37E-05
1 5E-04
33E-08
1 6E-05
7 1E4)7
7 IE 07
94E05
43EO5
1 4E 03
50E-06
47E-04
15E-05
34EO5
1 2E-04
3 2E-02
24E»00
9 1E-02
7 2E-02
7 2E-02
Subarea
N1 avg
N1 avg
Nt avg
N1 avg

N1 avg
N1 avg
Nt avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
N1 avg
Off-site
Vapor
Cone
(ug/m3)
4 IE 11
1 3E09
1 7E-10
2 7E 09
60E 09
34E05
5 9E 07
52E-06
21E05
46E-09
22E-06
9 9E-08
99E-08
1 3E-05
60E 06
20E-04
70E-07
66E-05
21E-06
46E-06
1 7E-05
45E 03
34E-01
1 3E-02
1 OE-02
1 OE-C2
Cancer
Adult
Dose
(mg/kgd)
1 4E 15
46E 14
60E 15
93E 14
2 1E-13
1 2E 09
2 IE 11
1 8E-10
74E 10
1 6E-13
79E-11
35E 12
35E 12
46E 10
21E 10
69E-09
25E-11
23E-09
74E-11
1 7E-10
59E-10
1 6E-07
1 2E-05
4 5E-07
3 5E 07
3 5E-07
Cancer
Child
Dose
(mg/kg-d)
36E 15
1 IE-IS
1 5E 14
23E 13
53E-13
29E09
52E-11
45E-10
1 8E-09
4 1E-13
20E-10
87E 12
8 7E-12
1 2E-09
53E-10
1 7E-08
6 IE-It
58E-09
1 8E-10
42E-10
1 5E-09
39E-07
30E-05
1 IE 06
8 8E-07
8 8E-07
Cancer
School-age
Dose
(mg/kg-d)
22E-15
69E 14
91E 15
1 4E 13
32E 13
1 8E-09
31E-11
27E 10
1 1E-09
2 4E-13
1 2E-10
53E-12
53E-12
70E-10
32E-10
1 OE-08
37E-11
3 5E-09
1 1E-10
25E-10
89E-10
2 4E-07
1 8E-05
6 8E-07
5 3E-07
5 3E-07
Cancer
Farmer
Dose
(mg/kg-d)
32E-15
10E-13
1 3E-14
2 1E-13
47E-13
26E-09
46E-11
41E-10
1 6E-09
36E-13
1 8E-10
78E 12
78E-12
1 OE 09
4 7E-10
1 5E-08
55E-11
51E-09
1 6E-10
37E-10
1 3E-09
35E-07
27E-05
10E06
7 9E-07
79E-07
Noncancer
Adult
Dose
(mg/kg-d)
1 IE 14
36E 13
47E 14
73E 13
1 6E-12
92E-09
1 6E-10
1 4E-09
5 BE -09
1 3E-12
6 IE 10
27E 11
27E 11
36E09
16E09
54E08
1 9E-10
1 BE -08
58E-10
1 3E 09
46E-09
1 2E-06
93E05
35E06
2 BE -06
28E-06
Noncancer
Child
Dose
(mg/kg-d)
42E 14
1 3E 12
1 7E 13
27E-12
61E-12
3 4E-08
60E-10
53E09
2 IE-OS
47E-12
23E09
1 OE 10
1 OE-10
1 3E-08
62E 09
2 OE-07
72E-10
6 7E-08
2 IE 09
49E-09
1 7E-08
46E-06
35E C4
1 3E-05
1 OE 05
1 OE-05
Noncancer 1
School-age
Dose
(mg/kg-d)
25E-14
6 IE 13
1 1E-13
1 6E-12
37E-12
2 1E-08
36E-10
32E09
1 SE-08
29E-12
1 4E-09
6 IE 11
6 IE 11
81E-09
37E-09
12E4)7
43E-10
4 1E-08
1 3E-09
29E09
1 OE-08
2 BE -06
2 1E 04
79E-08
62E-06
62E-06
Noncancer
Farmer
Dose
(mg/kgd)
1 IE 14
36E-13
4 7E-14
73E-13
1 6E 12
92E09
16E-10
14E09
5 BE 09
1 3E-12
6 IE 10
27E-11
27E-11
36E-09
16E09
54E-08
1 9E-10
1 BE 08
58E-10
1 3E-09
46E09
1 2E 06
93E05
S5E-06
2 BE -06
2 BE 06
 NOTES
   NA - Not applicable
   NF - Not found
   NT - No toxicity Information
   HQ • Hazard quotient
   HI  - Hazard Index
 Volume V. Appendix V-14
-------
TABLE 4  Average Inhalation Risks and Noncancer HQs in Subaipa Nt
CHEMICAL
1.2.3.7 8.9 HxCDF
1.2.34.6 7.8HpCDF
1,2.3.4. 7.8.9 HpCDF
OCDF
Dioxm TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (h«xaval«nt)
Chromium (trivalenl)
Copper
Lead
Mercury (and MeHg)
Mickel
Selenium
Silver
fhalllum
!lnc
hydrogen chloride
'otal nitrogen oxides (NOx)
'otal sulfur oxides (SOx)
'articulate matter
tesplrable participates
Inhalation
Slope
Factor
(mg/kg d)*-1
1 5E»04
1 5E»03
1 5E*03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA '
NA

NA
000035
0000263
0000125
0 004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
OE04
5E 05
6E 05
3E 03
3E 04
3E 03
25E 01
NA
NA
2 IE 05
50E 03
1 3E-03
1 3E 03
1 BE 05
75E 02
50E 04
NA
HA
NA
NF
Emission
Rate
(g'sec)
293E 10
9 30E 09
1 22E 09
1 89E 08
428E-08
2 4E 04
42E06
3 7E-05
1 SE 04
33E 08
1 6E-05
7 1E-07
7 1E-07
94E05
4 3E 05
1 4E 03
50E 06
4 7E-04
1 5E 05
34E05
1 2E 04
32E 02
24E«00
9 1E 02
7 2E 02
7 2E 02
Subarea
N1 avg
N1 avg
Nt avg
N1 avg

N1 avg
N1 »vg
N1 avg
N1 avg
N1 avg
N1 avg
N1 vg
N1 vg
N1 vg
N1 vg
N1 vg
N1 vg
N1 avg
N1 avg
N1 avg
N1 avg
Nt avg
Nt avg
N1 avg
N1 avg
N1 avg
Adult
Cancel
Risk
2 2E 11
69E 1 1
9 OE 1 2
1 4E-11
69E 10
NT
NT
9 IE 09
NT
1 4E 12
48E-10
1 4E-10
NT
NT
NT
NT
2 IE 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancel
Risk
S4E 11
1 7E 10
2 2E II
35E 11
1 7E 09
NT
NT
23E 08
NT
34E 12
1 2E 09
36E-10
NT
NT
NT
NT
52E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
33E 11
1 OE 10
1 4E 11
2 IE 11
1 OE 09
NT
NT
1 4E-08
NT
2 IE- 12
72E 10
22E-10
NT
NT
NT
NT
3 IE 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Faimer
Cancel
Risk
4 BE 11
1 5E 10
20E 11
3 IE 11
1 5E 09
NT
NT
20E 08
NT
30E 12
1 IE 09
32E-10
NT
NT
NT
NT
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
 IOTES.
  NA - Not applicable
  NF = Not found
  NT = No toxicity information
  HQ * Hazard quotient
  HI » Hazard index
                                                                               Total Risk    1 5E-08    3 BE-08    2 3E-08    3 4E-08
                                                                                                                                              Adult      Child    School age  Faimer
                                                                                                                                            Noncancer  Noncancer  Noncancer Noncancer
                                                                                                                                               HO        HQ        HQ        HQ
NT
NT
NT
NT
NT
NT
1 6E-06
19E05
1 6E 04
1 OE-09
49E 06
2 2E 08
1 1E-10
NT
NT
2 5E 03
3 BE 08
1 4E 05
46E^)7
74E05
61E^>8
25E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E06
7 IE 05
60E 04
38E09
1 8E 05
8 IE 08
41E-10
NT
NT
94E-03
1 4E 07
54E05
1 7E 06
2 BE 04
2 3E 07
92E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E06
43E 05
36E4)4
23E-09
1 1E^)5
A 9E-08
25E-10
NT
NT
57E4)3
87EX18
33E^»
10E-06
1 7E^)4
1 4E4)7
55E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E 06
1 9E 05
1 6E 04
10E 09
49E06
2 2E 08
1 1E-10
NT
NT
25E 03
38E 08
1 4E 05
46E 07
74E^B
6 1E 08
2 5E-03
NT
t4T
NT
NT
                                                                                                                                   Total HI   59E-03   2 2E 02   1 3E 02   5 9E 03
  ilume V. Appendix V-' '
-------
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-------
TABl E 5  Avetage Inhalation Risks and Noncanror HOs in S abate* a 1
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrylonrtrile
Anthracene
Benzene
Benzole acid
Benzotrichlorlde
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)nuoranthene
Benzo(g,h.l)p«rylene
Benzo(k)fluoranthene
Bls(2-chloro«thoxy) methane
Bis(2-chloto«1hyl)ether
Bis(2-chloioisopropyl)ethef
Bis(2-ethy1hexyl)phthalale
Bromodlchloromethane
Bromo(orm
Bromomethane
B'omodipheny) ether p
Butanone. 2- (Methyl ethyl kelone)
ButylberurylphUialate
Carbon disurfide
Carbon telrachloride
Chlordane
Chloro-3-methylph«nol. 4
Chloroaniline. p- (4-Chloroanilme)
Chlorobenzen*
Chlorobenzllat*
Chloroethane (Ethyt chloride)
Chloroform
Chloromethane
Chloionaphthalene. beta
Chloiophenol. 2-
Chlorodiphenyl ether. 4-
Chrysene
Cresol. m-
Cresol. o- (2-Methylphenol)
Cresol, p-
Crotonaldehyde
Cumene
DDE. 4.4'-
Dibenz(a .(i)anthracene
Dibromochloromethane
Dichloiobenzene. 1.3-
Dichlorobenzene. 1,4-
Dichlorobenzene. 1.2-
Dichlorobenzidme 33'-
Dichloiobiphenyl
Inhalation
Slope
Faclor
(mg/kg d)"-1
NA
NF
7 7E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E 03
NA
NA
NA
NA
NA
5 3E 02
1 3E«00
NF
NA
NA
2 7E-01
NA
8 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg)m3)
00525
NF
0 00225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
2 5E 02
1 4E-04
75E-02
4 3E-04
1 OE»00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E03
50E-03
36E 04
NA
7 IE 02
50E 02
7 1E 04
1 4E 04
1 5E-05
NF
1 OE 03
1 4E 03
5 OE-03
7 1E-01
2 5E-03
NA
20E 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
64E 04
HA
NA
50E 03
NA
57E 02
1 4E 02
tJA
HA
Emission
Rate
(g/sec)
67E 06
67E06
30E04
2 9E-03
29E04
2 OE 04
55E06
1 5E 05
' 1 1E05
32E-05
55E08
55E06
55E06
55E06
55EO6
67E4J6
1 3E-05
67E06
3 7E 05
1 OE-04
55E06
4 9E-04
67EW
5 1E-05
55E06
89E05
1 6E 04
55E 07
67E06
67E06
55E06
3 7E 05
4 9E-04
2 7E 04
25E 04
67E-06
55E06
67E 06
55E06
55E 06
5 5E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subaiea
N2avg
N2avg
N2 avg
N2avg
N2 avg
N2avg
N2avg
N2 avg
N2 avg
N2avg
N2»vg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2 avg
N2 avg
N2 avg
N2 avg
f J2 avg
N2 avg
N2 avg
N2 avg
til avg
(12 avg
N2 avg
Adult
Cancer
Risk
NT
NT
45E-12
NT
NT
93E-11
NT
83E-13
NT
NT
NT
NT
NT
NT
NT
NT
28E-11
NT
NT
NT
4 1E-14
NT
NT
NT
NT
NT
16E-11
1 4E-12
NT
NT
NT
1 9E-11
NT
4 1E-11
30E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
tIT
fJT
NT
W
m
Child
Cancer
Risk
NT
NT
1 1E-11
NT
NT
23E 10
NT
2 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
7 1E-11
NT
NT
NT
1 OE-13
NT
NT
NT
NT
NT
40E-11
34E-12
NT
NT
NT
48E-11
NT
1 OE-10
74E-12
NT
NT
NT
NT
NT
NT
f4T
fJT
NT
UT
UT
m
HI
MT
fJT
UT
m
School age
Cancer
Risk
NT
NT
68E-12
NT
NT
1 4E-10
NT
1 2E 12
NT
NT
NT
NT
NT
NT
NT
NT
43E-11
NT
NT
NT
62E-14
NT
NT
NT
NT
NT
24E 11
2 IE 12
NT
NT
NT
29E-11
NT
62E-11
45E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
nr
nr
(IT
m
nr
m
nr
Farmer
Cancel
Risk
NT
NT
10E-11
NT
NT
2 1E-10
NT
1 8E-12
NT
NT
NT
NT
NT
NT
NT
NT
63E 11
NT
NT
NT
9 IE 14
NT
NT
NT
NT
NT
36E 11
31E-12
NT
NT
NT
43E-11
NT
92E-11
66E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
nr
nr
nr
UT
(IT
nr
                                                                                                                                                 Adult      Child    School age   Farmer
                                                                                                                                              Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                                 HQ        HQ        HQ       HQ
67E-09
NT
7 IE -06
1 7E-06
1 8E-07
2 IE-OS
1 IE 09
52E-07
1 7E-10
NT
NT
NT
NT
NT
NT
NT
NT
10E 08
1 IE 07
3 IE 07
1 7E-OB
2 1E^>5
NT
1 IE 08
1 7E 09
19E 06
1 7E-05
5 5E-07
NT
1 OE 07
5 BE 08
1 IE 07
1 OE 08
16E-06
NT
50E-09
66E-08
NT
NT
66E 09
6 BE 09
66E 08
NT
1 3E 07
NT
NT
7 9E 08
NT
1 4E 09
5BF 09
tit
fir
2 5E 08
NT
26E 05
65E 06
6 6E 07
80E 05
4 IE 09
19E06
64E-10
NT
NT
NT
NT
NT
NT
NT
NT
38E 08
4 2E 07
12E06
62EOB
77E^»
NT
4 IE 08
62E 09
70E06
62E 05
2 1E 06
NT
3 BE 07
2 2E 07
4 1E 07
39E 08
6 OF. 06
NT
1 9E 08
2 5E 07
NT
NT
25E 08
25E 08
25E 07
NT
4 BE 07
MT
nr
3 OF 07
tit
5 4( 09
2 71 m
in
111
1 5E 08
NT
1 6E 05
39E 06
40E07
4 BE 05
25E 09
1 2E 06
38E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 3E 08
25E 07
7 OE-07
3 7E-08
4 7E 05
NT
24E 08
37E 09
42E06
3 BE 05
1 2E 06
NT
23E 07
1 3E 07
25E07
2 3E 08
36E 06
NT
1 1E 08
1 5E 07
NT
NT
1 5E 08
1 5E 08
1 5E 07
NT
79E-07
NT
ra
1 BE -07
NT
33E 09
1 IE 08
(IT
m
6 7E-09
NT
7 IE 06
1 7E-06
1 BE 07
2 IE-OS
1 IE 09
52E07
1 7E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 OE 08
1 1E 07
3 1E 07
1 7E 08
2 1E 05
NT
1 IE 08
1 7E09
19E06
1 7E05
55E-07
NT
1 OE 07
5 BE 08
1 IE 07
1 OE 08
1 6E 06
NT
50E 09
66E-08
NT
NT
66E 09
66E 09
6 RE 08
NT
1 3E 07
NT
NT
7 9E 08
NT
1 4E 09
5 BE -09
UT
NT
/olume V Appendix V-'
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-------
T ABl E 5  Average Inhalation Risks and Nonc.incer HQs in Subaroa N2
CHEMICAL
Dichlorodifluoromethane
Dichloroethane. 1.1- (Ethylidene dichloride)
Dichlotoettiana. 1,2-
Dichloioethene. 1,1- (Vmylidine chloride)
Dichloroelhene (trans). 1 .2-
Oichlorophanol. 2,4-
Dichloropropane. 1 .2- (Propylene dichloiide)
Dlchtoropropena (cis). 13
Otchloropropene (bins). 1 .3-
Dlethylphlhalate
Dlmethoxyfoenzidina. 3.3'-
Dlmathylphenoi. 2.4-
Dimethylphlhalate
D( n-butylphth»lat«
Dlnlbotoluena. 2.6-
Dinltio-2-methylphenol. 4.6-
Dlnlbophenol. 2.4-
Dinitrotoluene. 24
Dioxana. 1.4
Di(n)octyl phttialal«
D. 2.4-
Etfiyl methacrylate
£thytb«nzana
Ethylene dibromlde
Ethylana oxide
Sthytana thlouraa
:luoranthana
-luoi»n»
rormaldehyde
rurfutal
leptachlor
-laptachloroblphanyl
texachlorobenzena
texachloroblphanyl
Texachtorobutadlena
^axachlofocyclohexana, gamma (Lindane)
taxachlorocyclopentadiene
lexachloroe thane
r OS
in
26E 07
53E 09
NT
8 4E 08
38E 08
1 IE 07
66E 07
1 3E 07
1 3E 07
1 3E 09
NT
1 7E-08
NT
94E09
33E 07
NT
1 7E 07
1 7E 07
NT
1 7E 08
23E07
1 6E 07
1 IE 07
1 2E 04
NT
1 1E 10
83E09
1 OE OS
t BE 07
23E OB
66E 08
NT
4 1E 07
NT
30E 05
1 IE 05
1 7E 05
33E 07
64E 06
NT
NT
20E 09
1 4E 08
66E09
88E 10
33F 08
28F 08
(It
NI
8 3E 09
7 If 06
NI
       V Appendix V 14
-------
                Inhoio
TABLE 5  Average Inhoiaiion Risks and Noncancer HQs in Subarea N2
CHEMICAL
Nitroanlline. 4-
Nitrobenzene
Nitrophenol. 2-
Niltopheno). 4-
N-Niuoso-dt-n-butylamine
N-Nitroso-di-n-propylamlne
N Nrtrosodlphenylimln* (Dtphenylamlne)
Nonachkwoblphenyl
OctachkMobiphenyl
Pentachlorobenzene
Pentachtorobiphenyt
Pentachloronrtrobenzen*
Pentachlorophenol
Phenanthrene
Phenol
Pytene
Safrole (5-(2-Propenyl)-1 ,3-benzodk>xole)
Styrene
Tetrachlorobiphenyl
Tebachloroethane, 1.1.1.2-
Tebachloroelhane. 1,1.2.2-
Tebachloroelhene
T»b»chloroph«nol. 2,3.4.6-
Toluene
Trichk>ro-1.2.2-bifluaroethane. 1.1.2
Trkhlorobtwuene, 1,2.4-
Trlchloroblphenyl
Trichtoroethane. 1,1.1- (Methyl chloroform)
Trichloroeu-.ane. 1 .1 .2-
Trlchloro«thene
Tttehlorofluoromethane
Trtehlorophenol, 2.4.5-
Trlchlorophenol, 2,4.8-
\flnyl acetate
Vinyl chloride
Xylen*. nVp- (m/p-Dimethyl benzene)
Xylene, o- (o-Dlmethyl benzene)
2.3.7,8-TCDD
1.2.3.7.8-PCDD
1 2 3 4.7,8 HxCDO
1.2.3,6.7.8 HxCDO
1. 2.3.7.8.9 HxCDD
1.2,3.4.6.7.8-HpCDD
OCOD
2.3.7,8 TCDF
1.2.3.7,8-PCDF
2.3.4.7.8 PCDF
1 234.7.BHxCDF
1.2.36.7.8HxCDF
2.34.6.7,8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)M
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E 02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
606-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
15E+05
7 5E«04
1 5E+04
1 5E»04
1 5E»04
1 5E+03
1 5E«02
1 5E + 04
75E»01
75E+04
t 5E»04
1 5E»04
1 5E+04
RAC
(mg/m3)
NF
00005
NF .
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
002625
NA
0525
002625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
75E-03
NF
7 1E-02
NA
75E-03
NA
25E 03
75E^)3
29E-02
2 1E+00
1 4E-02
NA
71E4)2
1 OE-03
NA
5 OE-02
2 5E-02
NA
1 4E-02
NA
50E 01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
IIA
NA
NA
IIA
NA
Emission
Rate
(B/sec)
67E46
55E06
67E06
55E06
1 2E-04
67E-06
67E-06
t 4E-08
14E08
4 BE -05
1 4E-08
34E-05
S5E-06
87E-06
55E-06
55E-06
12E-04
23E-05
1 4E-08
55E-06
55E-06
5 IE-OS
6 BE -06
6 IE 04
3 3E-04
55E-06
30E-08
1 3E-05
1 3E-05
1 9E-05
2 5E-04
55E-06
55E-06
64E-05
25E 04
3 BE 04
55E-06
1 08E 11
6 78E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
3 45E 10
467E to
1 43E 09
1 33E 09
1 50E 09
Subarea
N2 avg
N2avg
N2avg
N2svg
N2 avg
N2avg
N2avg
N2 avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2ivg
N2 avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2 avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 Jvg
N2 avg
N2 avg
N2 avg
112 avg
N2 avg
N2 avg
IJ2 avg
N2 avg
112 avg
112 avg
112 avg
Of! site
Vapor
Cone
(ug/m3)
3 7E 07
3 OE 07
3 7E 07
30E07
67E06
37E07
3 7E-07
77E-10
77E 10
26E-06
7 7E-10
1 9E-06
3 OE-07
3 7E-07
3 OE 07
3 OE-07
63E06
1 2E-06
7 7E-10
30E 07
3 OE 07
26E-06
3 7E 07
34E^>5
1 BE -05
3 OE-C7
1 7E 09
69E-07
6 9E-07
1 OE 06
1 3E-05
3 OE-07
3 OE-07
3 5E 06
1 3E 05
2 IE 05
3 OE 07
59E 13
37E 12
49E 12
9 IE 12
60E 12
6 BE 11
3 4E 10
4 BE 12
1 9E 11
26E II
7 BE 11
7 3E 11
8 3E 11
Cancer
Adult
Dose
(mg/kg-d)
1 3E 11
1E-11
3E-11
IE 11
3E 10
3E-11
3E-11
27E-14
27E 14
92E-11
27E 14
65E-11
1 1E-11
1 3E-11
1 1E-11
1 1E-11
22E-10
44E 11
27E-14
1 1E-11
1 IE 11
99E-11
1 3E-11
1 2E-09
64E-10
1 1E-11
59E-14
24E 11
24E-11
36E-11
47E 10
1 1E-11
1 1E-11
1 2E-10
47E-10
74E 10
1 1E-11
2 IE 17
1 3E 16
1 7E 16
32E 16
2 IE 16
24E 15
1 2E 14
1 7E 16
6 7E 16
90E 16
2 BE 15
26E 15
29E 15
Cancer
Child
Dose
(mg/kg-d)
32E-11
27E 11
32E 11
27E 11
58E-10
32E-11
32E 11
6BE-14
6BE-14
23E-10
6 BE 14
1 6E-10
27E-11
32E-11
27E-11
27E-11
55E-10
1 1E-10
6BE-14
27E-11
27E-11
25E-10
33E-11
30E-09
16E-09
27E-11
15E-13
60E-11
60E-11
90E-11
1 2E-09
27E-11
27E-11
31E-10
12E09
1 BE 09
27E-11
52E 17
33E 16
43E 16
60E 16
53E 16
60E 15
30E 14
4 2E 16
1 7F 15
2 3E 15
69E 15
64E 15
7 3E 15
Cancer
School age
Dose
(mg/kg-d)
20E 11
1 6E-11
20E 11
16E-11
35E-10
20E-11
20E-11
4 IE 14
4 1E-14
1 4E 10
4 IE 14
98E-11
16E-11
20E-11
16E-11
16E-11
34E-10
66E-11
4 1E-14
16E 11
1 6E-11
1 5E 10
20E-11
18E-09
96E-10
16E-11
88E-14
36E-11
36E-11
54E-11
71E-10
16E-11
16E 11
1 9E-10
71E-10
1 IE 09
1 6E-11
31E 17
20E 16
26E 16
4 BE 16
32E 16
36E 15
1 BE 14
26E 16
1 OE 15
1 4E 15
4 2E 15
39E 15
44E 15
Cancer
Farmer
Dose
(mg/kg-d)
29E-11
24E-11
29E 11
24E-11
52E-10
29E-11
29E-11
60E-14
60E-14
20E-10
60E-14
1 5E-10
24E-11
29E-11
24E-11
24E-11
49E-10
97E 11
60E-14
24E 11
24E-11
22E 10
29E-11
26E09
ME 09
24E-11
1 3E-13
54E 11
54E-11
80E-11
1 1E-09
24E-11
24E-11
2BE-10
1 IE 09
16E09
24E-11
4 BE 17
29E 16
39E-16
7 IE 16
47E 16
53E 15
26E" 14
38E 16
1 5E 15
20E 15
6 IE 15
5 7E 15
65E 15
Noncancer 1
Adult
Dose
(mg/kg-d)
1 OE-10
BSE 11
1 OE-10
B3E-11
1 BE -09
1 OE-10
1 OE-10
21E-13
21E-13
72E 10
21E-13
51E-10
83E-11
1 OE-10
83E-11
83E-11
1 7E 09
34E-10
21E-13
83E-11
83E-11
77E-10
10E 10
92E09
50E-09
83E-11
46E-13
1 9E-10
19E-10
28E-10
37E-09
83E-11
83E 11
97E-10
37E-09
5 7E-09
83E-11
1 6E 16
10E 15
1 3E 15
25E 15
1 6E 15
1 9E 14
93E 14
1 3E 15
52E 15
70E 15
2 1E 14
2 OF. 14
2 3F 14
Noncancer Noncancer 1
Child School-age
Dose Dose
(mg/kg-d) (mg/kg-d)
38E-10 23E-10
31E-10 1 9E-10
38E-10 23E-10
3 IE 10 1 9E-10
68E-09 4 1E-09
38E-10 23E-10
38E-10 23E-10
79E13 48E-13
79E-13 48E-13
2 7E-09 1 6E-09
79E-13 4 BE 13
1 9E-09 1 1E-09
31E-10 19E-10
3BE-10 23E-10
3 IE 10 1 9E 10
3 IE 10 1 9E-10
6 5E-09 3 9E-09
1 3E-09 7 7E-10
79E-13 48E-13
31E-10 19E-10
31E-10 19E10
2 9E-09 1 7E-09
38E-10 23E10
34E-08 2 1E-08
1 9E-OB 1 IE 08
31E-10 1 9E-10
1 7E-12 10E-12
7 OE-10 43E-10
7 OE-10 43E-10
1 OE 09 6 3E-10
1 4E-08 8 3E 09
31E-10 19E-10
31E-10 1 9E-10
36E-09 22E-09
1 4E 08 8 3E 09
2 IE 08 1 3E 08
31E-10 1 9E-10
6 IE 16 3 7E 16
3 BE 15 2 3E 15
50E 15 30E 15
93E 15 56E 15
6 IE 15 3 7E 15
70E 14 42E 14
35E 13 * 2 IE 13
49E 15 30E 15
1 9E 14 1 2E 14
26E 14 1 6E 14
80E 14 48E 14
7T>E 14 45E 14
8f>F 14 5 IE 14
Noncancer
Farmer
Dose
(mg/kg-d)
1 OE 10
83E 11
1 OE-10
83E-11
1 BE 09
1 OE-10
1 OE-10
21E 13
2 IE 13
72E-10
2 IE 13
51E-10
83E-11
1 OE-10
B3E-11
83E 11
1 7E-09
34E 10
21E 13
B3E 11
83E 11
77E-10
1 OE-10
92E-09
50E-09
83E 11
46E-13
1 9E-10
1 9E-10
2 BE 10
37E09
B3E-11
83E 11
97E 10
37E09
57E09
B3E-11
1 BE 16
1 OE-15
1 3E 15
25E 15
1 6E 15
1 9E 14
93E 14
1 3E 15
52E 15
70E 15
2 IE 14
20E 14
2 3P 14
Volume V. Appendix V-14
-------
TABLE 5  Average Inhalation Risks and Noncancer HQs in Suhaica M2
CHEMICAL
Nitroaniline, 4-
Nitrobenzene
Nitrophenol. 2-
Nrtrophenol, 4-
N Nrtroso-di-n-butylamine
N Nrtroso-di-n-propylamme
N-Nrtrosodlphenylamine (Diphenylamine)
Nonac hlof obiphenyt
Octachloroblphenyl
Pentachloroberuene
Pentachlorobiphenyl
Pentachloronltrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Pyrene
Safiole (5-(2 Propenyt) 1 .3 benzodioxole)
Styrene
retrachlorobiphenyl
Tetiachloroethane. 1.1,12
Tetrachloroelhane. 1.1.22
Tetrachloroethane
Tetrachlorophenol. 2.3.4.6
Toluene
frichloro- 1 .2.2 trifluoroethane 1.1.2-
rrfchlorobenzene, 1.2,4-
frichiorobiphenyl
rtchloroethane, 1,1.1- (Methyl chloroform)
rrlchloroethane. 1,1.2-
richloroethene
ri-hlorofluoromethane
frichlorophenol, 2.4,5-
richlorophenol. 2,4.6-
rtnyl acetate
finyl chloride
!ylen«, m/p- (m/p-Dimethyl benzene)
iylene. o- (o-Dimethyl benzene)
,3.7.8-TCDD
.2.3.7.8 PC DD
.2 3 4. 7.8 HxCDD
2 3.6 7.8 HxCDD
23789 HxCDD
.2.3,46.78 HpCDD
>CDD
3.78 TCDF
2378 PCDF
347 8 PCDF
? 3 4 7.8 HxCDF
. 3678 HxCDF
34678 HxCDF
Inhalation
Slope
Factor
(mg/kgdC-1
NF
NA
NF
NF
54E«00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
60E 03
NA
NA
1 OE-02
NA
30E 01
NA
NA
1 5E+05
7 5E*04
5E+04
5E«04
5E»04
5E«03
5E»02
5E»04
75E+03
75E«04
5E«04
5£«04
1 5E«04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
Inhalation
RID
(mg/kg-d)
NF
1 4E 04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E 04
7 5E-03
NA
1 5E-01
75E-03
NF
7 1E-02
NA
75E-03
NA
25E 03
75E 03
29E 02
2 1E«00
1 4E-02
NA
7 IE 02
1 OE-03
NA
50E 02
2 5E-02
NA
1 4E-02
NA
50E-01
50E 01
NA
NA
NA
NA
NA
rw
NA
NA
NA
NA
NA
NA
UA
Emission
Rate
(g/sec)
6 7E 06
55E 06
6 7E 06
55E 06
1 2E-04
6 7E 06
67E 06
1 4E-08
'1 4E 08
4 BE 05
1 4E 08
34E 05
55E-06
67E 06
55E-06
55E-06
1 2E 04
23E 05
1 4E 08
55E-06
55E 06
5 1E 05
68E-06
6 IE 04
3 3E 04
55E-06
3 OE 08
1 3E 05
1 3E-05
1 9E 05
2 5E-04
55E 06
55E 06
64E 05
25E04
3 BE 04
55E 06
1 08E 11
6 78E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
4 67E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
, N2 avg
N2 avg
N2 avg
U2avg
t!2 avg
H2 avg
N2avg
N2 avg
112 avg
tJ2 a^g
N?avg
Adult
Cancer
Risk
NT
NT
NT
NT
1 3E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E-13
22E 12
20E-13
NT
NT
NT
NT
NT
NT
1 4E 12
2 1E-13
NT
NT
1 1E-13
NT
1 4E-10
NT
NT
3 1E 12
98E 12
26E 12
48E 12
32E 12
36E 12
1 BE 12
2 5E 12
50E 12
6 BE 11
4 IE 11
39E M
4 4E 11
Child
Cancer
Risk
NT
NT
NT
NT
32E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
69E 13
54E 12
50E-13
NT
NT
NT
NT
NT
NT
34E-12
54E-13
NT
NT
2 7E-13
NT
35E-10
NT
NT
7 BE 12
25E 11
65E 12
1 2E 11
79E 12
90E 12
4 4E 12
6 3E 12
1 2E 11
1 7E 10
1 OE 10
9 7E 11
1 IE 10
School age
Cancer
Risk
NT
NT
NT
NT
1 9E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
42E 13
33E 12
30E-13
NT
NT
NT
NT
NT
NT
2 1E-12
32E-13
NT
NT
16E-13
NT
2 1E-10
NT
NT
4 7E 12
1 5E 11
39E 12
72E 12
48E 12
54E 12
2 7E 12
3 BE 12
75E 12
1 OE 10
6 2E 11
5 BE It
6 fit 11
Farmer
Cancer
Risk
NT
NT
NT
NT
2 BE -09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
61E-13
4 BE 12
45E-13
NT
NT
NT
NT
NT
NT
3 IE 12
4BE-13
NT
NT
24E-13
NT
32E-10
NT
NT
70E 12
22E 11
58E 12
1 IE 11
70E 12
80E 12
40E 12
5 7E 12
1 IE 11
1 5E 10
9 2E 11
8GE 11
9 7E II
                                                                                                                                               Adull      Child   School age  Faimei
                                                                                                                                             Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                                HQ        HQ        HQ        HQ
NT
5 BE 07
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 8E 07
1 1E-08
NT
55E 10
1 1E-08
NT
47E-09
NT
1 IE-OS
NT
31EX)7
14E^»
32E07
23E-09
58E49
NT
26E^9
19E-07
NT
74E 08
33E-09
NT
68E-08
NT
1 IE 08
1 7E 10
NT
NT
NT
NT
NT
m
m
NT
NT
NT
NT
NT
III
NT
22E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E06
4 IE 08
NT
2 IE 09
4 IE 08
NT
1 8E-08
NT
4 1E48
NT
1 2E 06
5 IE 08
1 2E06
87E09
22E08
NT
9 BE 09
70E 07
NT
2 BE 07
1 2E-08
NT
25E 07
NT
43E 08
62E 10
NT
NT
NT
NT
NT
HI
NT
rn
NT
NT
NT
TIT
HI
NT
1 3E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E-06
25E-08
NT
1 2E-09
25E-08
NT
1 1E-08
NT
25E-08
NT
70E-07
31E^)8
73E^)7
52E09
1 3E-08
NT
60E09
43E^)7
NT
1 7E 07
75E-09
NT
1 5E 07
NT
26E OB
37E 10
NT
NT
NT
NT
NT
fIT
NT
NT
rn
NT
NT
NT
IIT
NT
58E 07
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 8E 07
1 1E-08
NT
55E 10
1 IE 08
NT
4 7E-09
NT
1 IE 08
NT
3 IE 07
1 4E 08
32E^)7
23E 09
5 BE -09
NT
26E 09
1 9E4)7
NT
74E 08
33E 09
NT
6 BE 08
NT
1 IE 08
1 7E 10
NT
NT
NT
NT
NT
NT
NT
NT
m
Nl
NT
NT
rn
 jlume V, Appendix V-*
-------
TABLE 5  Average I,
                      on Risks and Noncancei HQs in Subaiea N2
CHEMICAL
1.2.3.7.8.9-HxCDF
1,2.3.4,6,7.8-HpCDF
1,2.3.4.7.8.9-HpCDF
OCDF
Dtoxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (nexavilent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Resplrabie particulars
Inhalation
Slope
Factor
(mg/kg-d)«-1
1 5E«04
1 5E»03
1 5E»03
1 5E+02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA ..
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
IDE -04
75E-05
36E-05
1 3E 03
1 3E-04
1 3E-03
25E-01
NA
NA
2 IE-OS
50E 03
1 3E-03
1 3E-03
1 8E 05
75E-02
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
9 30E-09
1 22E 09
1 89E-08
4 28E-08
24E-04
42E-06
37E05
1 5E-04
33E-08
16E^»
7 1E-07
71E07
94E-05
43E-05
1 4E4>3
50E-06
47E-04
1 5E-05
34E-05
1 2E^4
3 2E-02
24E+00
91E-02
72E-02
72E-02
Subarea
N2avg
N2avg
N2avg
N2avg

N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
On-site
Vapor
Cone
(ug/m3)
1 6E-11
5 1E-10
67E-11
1 OE-09
24E-09
1 3E-05
2 3E-07
20E-06
83E-06
18E-09
8 8E-07
39E-08
39E-08
52E-06
24E-06
77E-05
28E-07
26E-05
83E-07
1 9E-06
66E-06
1 8E-03
1 3E-01
5 OE-03
4 OE-03
4 OE-03
Cancer
Adult
Dose
(mg/kg-d)
57E-16
1 BE 14
24E-15
37E-14
83E-14
46E-10
81E-12
72E-11
29E 10
64E-14
31E-11
14E-12
1 4E-12
1 8E-10
83E-11
27E-09
97E-12
91E-10
29E-11
66E-11
23E-10
6 2E-08
47E-06
1 8E-07
1 4E-07
1 4E-07
Cancer
Child
Dose
(mg/kgd)
1 4E 15
45E 14
59E-15
91E-14
2 1E-13
1 2E-09
20E-11
1 8E-10
72E-10
16E-13
7 7E-11
34E-12
34E-12
45E 10
21E 10
6 BE -09
24E-11
23E-09
72E-11
1 6E-10
58E-10
1 5E-07
1 2E-05
4 4E-07
3 5E-07
3 5E-07
Cancer
School-age
Dose
(mg/kg-d)
85E-16
2 7E-14
36E-15
55E-14
1 2E-13
70E-10
1 2E-11
1 1E-10
44E-10
96E-14
47E-11
21E-12
21E-12
27E-10
1 3E-10
41E-09
1 5E-11
1 4E-09
44E-11
99E-11
35E-10
93E-08
7 1E-OC
27E-07
2 IE 07
2 1E-07
Cancer
Farmer
Dose
(mg/kg-d)
1 3E-15
40E-14
53E-15
82E-14
1 8E-13
1 OE-09
18E-11
1 6E-10
65E-10
1 4E-13
69E-11
31E-12
31E-12
40E-10
1 9E-10
6 OE-09
22E-11
2 OE-09
65E-11
t 5E-10
52E-10
1 4E 07
10E-05
3 9E-07
3 1E-07
3 1E-07
Noncancer
Adult
Dose
(mg/kgd)
44E 15
1 4E 13
1 BE-14
29E-13
64E-13
36E-09
63E-11
56E-10
23EX»
50E-13
24E-10
1 IE-11
1 IE-11
1 4E-09
65E 10
2 IE-OS
75E11
71E-09
23E 10
5 IE 10
18E-09
48E-07
38E-05
14E-06
1 1E-06
1 IE 06
Noncancer
Child
Dose
(mg/kg-d)
1 6E-14
52E-13
69E-14
1 1E-12
24E-12
1 4E-08
24E-10
21E-09
84E-09
1 9E-12
90E-10
40E-11
40E-11
53E-09
24E-09
79E-08
2 8E-10
26E-08
84E-10
19E-09
6 BE -09
1 BE -06
14E^4
51E-06
4 IE-OS
41E-06
Noncancet
School-age
Dose
(mg/kg-d)
1 OE-14
32E-13
42E-14
64E-13
1 5E-12
82E-09
1 4E-10
1 3E-09
51E-09
1 1E-12
54E-10
24E-11
24E-11
32E09
1 5E-09
4 BE -08
1 7E-10
1 6E 08
5 IE 10
1 2E 09
4 1E-09
1 1E 06
B2E05
3 IE 06
24E06
24E-06
Noncancer
Farmer
Dose
(mg/kg-d)
44E-15
1 4E-13
1 8E-14
29E-13
64E-13
36E-09
B3E 11
56E-10
23E-09
50E-13
24E 10
1 IE 11
1 IE-11
1 4E 09
65E-10
2 1E-08
75E-11
71E4»
2 3E-10
51E-10
1 6E-09
4BE47
36E05
1 4E-06
1 1E-06
1 1E4»
NOTES:
  NA > Not applicable
  NF-Not found
  NT - No toxlctty Information
  HQ- Hazard quotient
  HI 'Hazardindex
Volume V, Appendix V-14
-------
TABLE 5  Average Inhalation Risks and Noneancei MQs in Siibaioa f J2
CHEMICAL
1 2.3.7,8.9 HxCDF
1.2.3. 4,6.7.8 HpCDF
;. 2. 3.47.8.9 HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivalenl)
Coppet
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paitculate mattw
Resplrable particulates
Inhalation
Slope
Factor
(mg/kg d)*-1
1 5E»04
1 5E«03
1 5E»03
1 5E»02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
OOO0075
00175
0004375
0004375
OOO0061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
10E-04
75E^»
36E 05
1 3E-03
1 3E 04
1 3EX)3
25E^)1
NA
NA
2 IE 05
50E.03
1 3E 03
1 3E-03
1 BE 05
7 5E-02
50E-04
NA
MA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E 09
1 89E 08
4 28E-08
2 4E-04
42E 06
3 7E 05
1 5E 04
3 3E 08
1 6E 05
7 1E 07
7 IE 07
94E 05
43E 05
1 4E 03
50E-06
4 7E 04
1 5E 05
34E-05
1 2E 04
3 2E 02
24E»00
9 IE 02
7 2E 02
7 2E 02
Subarea
N2avg
N2avg
N2 avg
N2avg

N2avg
N2avg
N2avg
N2avg
N2avg
N2 avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
N2avg
Adult
Cancel
Risk
85E 12
2 7E 11
35E 12
55E 12
2 7E-10
NT
NT
36E-09
NT
54E-13
1 9E-10
56E-11
NT
NT
NT
NT
8 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancel
Risk
2 IE-It
6 7E 11
8 BE 12
1 4E 11
68E 10
NT
NT
89E-09
NT
1 3E 12
4 7E-10
1 4E-10
NT
NT
NT
NT
20E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancel
Risk
1 3E 11
4 IE-It
53E 12
83E 12
4 1E 10
NT
NT
54E-09
NT
8 IE 13
28E-10
BSE 11
NT
NT
NT
NT
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Faimei
Cancel
Risk
1 9E 11
60E 11
79E 12
1 2E 11
6 1E 10
NT
NT
80E-09
NT
1 2E 12
42E-10
1 3E-10
NT
NT
NT
NT
1 8E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                               Adult      Child   School age   Famiei
                                                                                                                                             Noneancei Noneancei Noneancei Noneancei
                                                                                                                                                HQ       HQ       HO        HQ
NT
NT
NT
NT
NT
NT
63E-07
74E06
63E-05
40E 10
1 9E-06
86E 09
43E-11
NT
NT
9 8E-04
1 5E-08
57E06
1 8E 07
29E^»
2 4E-08
96E-04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
24E 06
2 BE 05
2 4E 04
1 5E 09
72E06
3 2E 08
1 6E-10
NT
NT
37E03
S 6E 08
2 1E 05
68E 07
t tE 04
90E 08
36E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
t 4E 06
1 7E 05
t 4E 04
90E 10
44E-06
1 9E 08
97E-11
NT
NT
2 2E 03
34E 08
1 3E-05
4 tE 07
66E 05
54E 08
2 2E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 3E 07
74E 06
6 3E 05
40E 10
1 9E 06
86E 09
43E-11
NT
NT
98E04
1 5E 08
57E06
1 8E 07
29E 05
24E 08
96E 04
NT
NT
HT
NT
                                                                                Total Risk   60E-09    1 5E-08    9 IE 09    1 3E 08
                                                                                                                                     Total HI    23E-03    8 7E 03    5 3E 03   2 3E 03
NOTES
  NA = Not applicable
  NF = Not found
  NT - No toxicity information
  HQ •= Hazard quotient
  HI = Hazard index
'olume V Appendix V '
-------
TABLE 6  Avefage Inhalation Risks and Noncancer HQs in Subarea N3
CHEMICAL
Acenaphlhene
Acenaphthylene
Acetaldehyde
Acetone
Acelophenone
Aciytonttrile
Anthracene
Benzene
Benzole acid
Benzotrlchlorlde
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Benzo(g,h ,l)perylene
Benzo(k)fluoranthene
Bls(2-chloroethoxy) methane
Bis(2-chloroethyl)ether
Bis(2-chloioisopropy1)ether
Bls(2-ethylhexyl)phlhai8te
Bromodichloromethane
Bromotorm
Bromomethane
Bfomodlphenyt ether, p-
Butanone, 2- (Methyl ethyt ketone)
Butylbenzylphlhaiate
Carbon disulflde
Carbon tettachlorlde
Chlordane
Chloro-3-methylphenol. 4-
Chloroanllfne. p- (4-Chloroanlline)
Chloroberuene
Chlorobenzilate
Chloroethane (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthalene, beta
Chlorophenol. 2- .,
Chlorodiphenyl ether, 4-
Chrysene
Cresol, m-
Cresol. o- (2-MethytphenoO
Cresol. p-
Crotonaldehyde
Cumene
DDE.4.41-
Dibenz(a ,h)antnracene
Dibromochloromethane
Dicnlorobenzene, 1.3-
Dichlorobenzene. 1,4-
Dichlorobenzene. 1.2-
Dichlorobenzidine. 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)*-1
NA
NF
7 7E-03
NA
NA
2 4E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
3 9E-03
NA
NA
NA
NA
NA
5 3E-02
1 3E*00
NF
NA
NA
27E-01
NA
8 1E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
0 00225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0 004375
NF
NA
004375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
« 4E-04
2 5E-02
2 5E-02
1 4E-04
7 5E-02
43E-04
10E+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE-02
50E-03
50E 03
50E-03
36E-04
NA
7 1E-02
5 OE-02
7 IE 04
1 4E-04
15E-05
NF
10E-03
1 4E-03
50E03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
13E02
1 3E 02
1 3E-03
NA
64E-04
NA
NA
50E03
NA
57E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E-06
67E-06
3 OE 04
2 9E-03
2 9E-04
20E-04
55E-08
1 5E-05
1 IE-OS
32E-OS
55E-06
55E-08
55E-06
55E-06
55E-06
67E-06
1 3E-05
67E-08
37E-05
10E-04
55E-06
49E-04
67E06
S1E-05
55E-06
89E-05
1 6E-04
5 5E-07
67E-08
67E-O8
55E-06
37E-05
4 9E-04
2 7E-04
25E-04
67E-06
55E-06
67E-06
55E-06
55E-06
55E-06
55E 06
1 4E 04
55E 06
55E 07
55E-06
26E-05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3ivg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3»vg
N3*vg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3 avg
f J3 avg
N3 avg
N3 avg
N3avg
N3avg
113 avg
N3 avg
Off-site
Vapor
Cone
(ug/rr>3)
1 6E 07
1 6E-07
72E-06
70E-05
70E-06
48E-06
1 3E-07
35E-07
27E-07
77E-07
13EX)7
1 3E-07
13E-07
1 3E-07
1 3E 07
1 6E-07
3 2E-07
1 6E-07
8 9E-07
25E-06
1 3E-07
1 2E-05
16E-07
1 2E-06
1 3E-07
21E-06
3 BE 06
1 3E-O8
16E-07
1 6E-07
1 3E-07
8 8E-07
1 2E-05
646-06
59E-06
1 6E-07
1 3E 07
1 6E-07
1 3E 07
1 3E 07
1 3E 07
1 3E 07
33E-06
1 3E 07
1 3E 08
1 3E 07
63E 07
1 3E 07
1 3E 07
1 3E 07
80E 07
1 1E 09
Cancer
Adult
Dose
(mg/kg-d)
57E-12
57E-12
25E-10
2 5E-09
25E-10
1 7E-10
46E-12
1 2E-11
95E-12
27E-11
46E-12
46E-12
46E-12
46E-12
46E 12
57E-12
1 1E-11
57E-12
31E-11
87E-11
46E-12
41E-10
57E-12
43E-11
46E-12
75E-11
1 3E-10
46E-13
57E-12
5 7E-12
46E-12
31E-11
41E-10
22E-10
21E-10
57E 12
46E-12
57E-12
46E 12
46E 12
46E 12
46E-I2
1 2E 10
46E 12
46E 13
46E 12
22E 11
46E 12
46E 12
46E 12
28E 11
40E-14
Cancer
Child
Dose
(mg/kg-d)
1 4E 11
1 4E-11
63E-10
61E-09
62E-10
43E-10
1 2E-11
31E-11
24E 11
67E-11
12E-11
12E-11
12E-11
1 2E-11
1 2E-11
1 4E-11
28E-11
1 4E-11
78E-11
22E-10
1 2E-11
10E-09
14E 11
1 1E-10
1 2E-11
1 9E-10
3 3E-10
1 2E-12
1 4E-11
1 4E-1I
1 2E-11
77E-11
1 OE-09
56E-10
52E-10
14E-11
1 2E-11
14E-11
12E-11
1 2E-11
1 2E 11
1 2E 11
29E 10
1 2E 11
1 2E 12
1 2E II
55E 11
1 2E 11
1 2E 11
1 2E 11
70E II
99E 14
Cancer
School- age
Dose
(mg/kg-d)
BSE 12
85E-12
38E 10
3 7E-09
37E-10
26E-10
70E-12
19E-11
1 4E-11
41E-11
70E-12
70E-12
70E-12
70E-12
70E-12
65E-12
17E-11
85E-12
47E-11
1 3E-10
70E-12
62E 10
85E-12
65E-11
70E-12
1 IE 10
20E-10
70E-13
B5E12
85E-12
70E-12
47E-11
62E-10
34E-10
31E-10
BSE 12
70E 12
85E 12
70E 12
70E-12
70E 12
70E 12
1 BE 10
70E 12
70E 13
70E 12
33E 11
70E 12
70E 12
7 OE 1 2
42E 11
60E 14
Cancer
Farmer
Dose
(mg/kg-d)
1 3E-11
1 3E-1 1
57E-10
5 4E-09
55E-10
3 BE 10
1 OE-1 1
28E-11
21E-11
60E-11
10E-11
10E-11
10E-11
10E-11
10E-11
1 3E-11
25E 11
1 3E-11
7 OE-1 1
t 9E-10
10E-11
92E-10
13E-11
97E-11
10E-11
1 7E-10
30E-10
10E-12
13E-11
1 3E-11
10E-11
69E-11
92E-10
50E-10
46E-10
13E 11
10E-11
1 3E-11
10E-11
10E-11
10E-11
10E-11
26E 10
1 OE 11
1 OE 12
1 OE 11
49E 11
10E 11
1 OE 11
1 OE 11
63E 11
88E 14
Noncancer 1
Adult
Dose
(mg/kg-d)
44E 11
44E-11
20E09
1 9E-08
19E-09
1 3E-09
36E-11
97E-11
74E-11
2 IE 10
36E 11
36E-11
36E-11
36E-11
36E-11
44E-11
87E-11
44E 11
2 4E-10
68E-10
36E-11
32E-09
44E-11
34E 10
36E-11
59E-10
1 OE-09
36E 12
44E 11
44E-11
36E11
24E 10
32E-09
1 7E-09
16E-09
44E-11
36E-11
44E 11
36E 11
36E-11
36E 11
36E-11
91E-10
36E 11
36E 12
36E 11
1 7E 10
36E 11
36E 11
36E 11
2 2E 10
3 1E 13
•Joncancei 1
Child '.
Dose
(mg/kg-d)
1 6E-10
1 6E-10
74E-09
7 IE 08
72E-09
5 OE-09
1 4E-10
36E-10
28E-10
7 9E-10
1 4E-10
1 4E 10
1 4E-10
1 4E-10
1 4E-10
1 6E-10
33E-10
1 6E-10
9 IE 10
25E-09
1 4E-10
1 2E-08
1 6E-10
13E09
1 4E-10
22E-09
39E-09
14E 11
1 6E-10
1 6E-10
1 4E-10
90E-10
1 2E 08
65E-09
6 OE-09
16E-IO
1 4E 10
16E-10
1 4E 10
1 4E 10
1 4E 10
1 4E 10
34E 09
1 4E 10
1 4E 11
1 4E 10
65E 10
1 4E 10
1 4E 10
1 4E 10
82E 10
1 ?F 12
Noncancer 1
School-age
Dose
(mg/kg-d)
99E-11
99E-11
4 5E-09
4 3E-08
43E-09
3 OE-09
82E 11
22E-10
1 7E-10
47E-10
82E11
82E-11
82E-11
82E-11
82E-11
99E-11
20E-10
99E11
55E-10
1 SE-09
82E-11
73E-09
99E 11
76E-10
82E 11
13E09
2 3E 09
82E 12
99E-11
99E 11
82E 11
55E 10
73E09
39E09
36E09
99E 11
82E 11
99E 11
82E 11
B2E-11
82E-11
82E-11
2 1E-09
82E 11
82E 12
82E 11
39E 10
82E 11
82E 11
82E 11
49E 10
70E 13
Joncancet
Farmer
Dose
(mg/kg-d)
44E 11
44E 11
20E09
'1 9E 08
19E-09
1 3E-09
36E-11
97E 11
74E-11
2 IE 10
36E-11
36E-11
36E-11
36E 11
36E 11
44E-11
87E-11
44E-11
2 4E-10
68E-10
36E-11
32E09
44E11
34E 10
36E 11
59E 10
10E09
36E-12
44E 11
44E 11
36E 11
24E 10
32E09
1 7E-09
16E-09
44E It
36E 11
44E 11
36E-11
36E It
36E 11
36E It
9 IE 10
36E 11
36E 12
36E 11
1 7E 10
36E 11
36E 11
36E 11
22E 10
3 IF 13
Volume V. Appendix V-14
-------
TABLE 6  Average Inhalation Ri-^s arid tJornJancci HOs in Subarra N3
CHEMICAL
Ac«naphthen«
Acenaphthylene
Acetaldehyde
Acetone
Acetophenona
Acrylonitril*
Anthracene
Benzene
Benzole acid
Benzotrichlorlde
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluor»nlhene
Benzo(p,h,l)perylene
Benzo(k)fluorinthene
Bls(2-«hloroethoxy) methane
Bi3(2 chloroethyl)ethei
9tj(2-chlorolsopropyl)ether
3ls(2-etnylhexyl)phthalale
Bromodlchloromethane
3romoform
Jromomethane
3romodiphenyl ether, p-
Jutanone, 2- (Methyl ethyl kelone)
)utytbenzylphthalate
Z»rbon dlsuffide
"arbon tetrachloride
Ihlordan*
'hloro-3-mothylphenol, 4-
xhloroanlline, p- (4-Chloroaniline)
;h>orobenzen«
'.hloiobenzllate
;hloroethane (Ethyl chloride)
;hloroform
"-hloromethane
",hloionaphth»lene, b«ta
;hlorophenol, 2-
;hlorodiphenyl ether. 4-
'.hrysene ";
:resol. m-
:resol. o- (2-Methylphenol)
.resol. p-
.rotonaldehyde
umene
iDE. 4,4'-
iib«nz(a,h)anthracene
iibromochloromethane
nchlorobenzene . 1 3
'ichlorobenzene. 1 4
•ichloroberuene, 1.2-
ichlorobenridme. 3 3 -
ichloiobiphenyl
Inhalation
Slope
Factor
(mg/Kg-d)A-1
NA
NF
7 7E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E«00
NA
NA
NA
39E 03
NA
NA
NA
NA
NA
53E02
1 3E+00
NF
NA
NA
27E-01
NA
8 1E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0 004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
2 5E 02
1 4E-04
7 5E 02
4 3E 04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E-03
50E 03
36E-O4
NA
7 1E 02
50E 02
7 IE- 04
t 4E 04
1 5E^)5
NF
1 OE-03
1 4E 03
5 OE 03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
64E 04
NA
NA
50E 03
^4A
5 7E 02
1 4E 0?
HA
UA
Emission
Rate
(9'»8C)
67E-06
6 7E 06
30E 04
2 9E-03
2 9E-04
20E 04
55E 06
15E05
1 IE 05
32E-05
55E06
55E-06
55E-06
55E06
55E06
67E-06
1 3E-05
87E06
3 7EO5
1 OE-04
55E06
49E04
87E-06
5 IE-OS
55E-06
89E05
1 6E 04
5 5E-07
67E 06
6 7E-06
55E 06
37E05
4 9E 04
2 7E 04
2 5E 04
67E 06
55E 06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
2 BE 05
55E 06
55E 06
55E 06
3 3E 05
4 7E 08
Subarea
N3avg
N3 avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
M3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3 avg
fJ3avg
N3 avg
H3avg
f!3avg
N3 avg
N3 avg
H3avg
N3 avg
Adult
Cancer
Risk
NT
NT
20E-12
NT
NT
4 1E-11
NT
36E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-11
NT
NT
NT
1 8E 14
NT
NT
NT
NT
NT
70E 12
60E 13
NT
NT
NT
85E-12
NT
t BE 11
1 3E-12
NT
NT
NT
NT
NT
NT
NT
NT
W
TJT
rir
MT
m
in
m
w
fJT
Child
Cancer
Risk
NT
NT
49E 12
NT
NT
1 OE-10
NT
90E-13
NT
NT
NT
NT
NT
NT
NT
NT
3 1E-11
NT
NT
NT
45E-14
NT
NT
NT
NT
NT
1 7E-11
1 5E-12
NT
NT
NT
2 1E 11
NT
45E-11
32E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Nf
NT
tJ!
tu
m
HI
tit
NT
School age
Cancer
Risk
NT
NT
29E-12
NT
NT
6 1E-11
NT
54E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 9E-11
NT
NT
NT
2 7E-14
NT
NT
NT
NT
NT
1 IE 11
9 1E-13
NT
NT
NT
1 3E-11
NT
2 7E-11
20E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
fir
NT
HI
m
m
HI
til
in
Fatmet
Cancer
Risk
NT
NT
44E-12
NT
NT
90E-11
NT
80E-13
NT
NT
NT
NT
NT
NT
NT
NT
27E-11
NT
NT
NT
40E-14
NT
NT
NT
NT
NT
16E 11
1 3E-12
NT
NT
NT
1 9E-11
NT
40E 11
29E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
NT
m
m
fJT
m
m
tn
Adult
Noncancer
HQ
29E 09
NT
3 1E-06
76E-07
7 7E-08
93E 06
48E 10
2 3E 07
74E-11
NT
NT
NT
NT
NT
NT
NT
NT
44E 09
4 9E 08
1 4E-07
72E09
90E 06
NT
47E09
72E 10
82E07
73E 06
2 4E-07
NT
44E 08
2 5E 08
4 BE 06
45E 09
7 OE-07
NT
22E09
29E-08
NT
NT
29E09
29E 09
2 9E 08
NT
56E 08
in
tn
3SF 08
MT
63E 10
2 5F 09
tn
rn
Child
Noncanc'"
HQ
1 1E 08
NT
1 IE 05
2 BE 06
29E 07
35E 05
1 BE 09
84E 07
28E 10
NT
NT
NT
NT
NT
NT
NT
NT
1 6E 08
1 8E 07
5 1E-07
2 7E 08
34E05
NT
1 BE 08
27E09
3 IE 06
2 7E-05
9 OE-07
NT
1 6E 07
9 5E 08
1 BE 07
1 7E 08
26E 06
NT
62E09
1 1E 07
NT
NT
1 IE 08
1 IE 08
1 IE 07
MT
2 IF 07
m
NT
1 11 07
fjf
2 4F 09
') 'if f)9
It!
Ill
School age
Noncancer
HQ
66E-09
NT
69E 06
1 7E-06
1 7E-07
2 IE-OS
1 IE 09
5 IE 07
1 7E-10
NT
NT
NT
NT
NT
NT
NT
NT
99E 09
1 IE 07
3 IE -07
1 6E 08
2 OE-05
NT
1 IE -OB
1 6E-09
1 9E 06
1 6E-05
54E-07
NT
99E 08
57E 08
1 IE 07
IDE 08
1 6E-06
NT
50E-09
65E-08
NT
NT
65E 09
65E 09
65E-OB
NT
1 'IF -07
NT
m
7 BF. 08
tit
1 4E 09
5 rf 09
Ml
NT
Farmer
Noncancer
HQ
29E 09
NT
3 IE 06
76E-07
7 7E 08
93E 06
4 BE 10
2 3E-07
74E-11
NT
NT
NT
NT
NT
NT
NT
NT
44E 09
49E 08
1 4E 07
72E 09
90E 06
NT
47E-09
72E 10
82E 07
73E-06
24E-07
NT
44E 08
25E 08
48E 08
45E-09
7 OE-07
NT
22E 09
29E 08
NT
NT
29E 09
29E 09
29E-OB
NT
5 6F. 08
NT
NT
35F 08
tu
63F 10
25F 09
tn
in
 )lume V Appendnt V
-------
TABLE 6  Average Inhalation Risks and Noncancer HOs in Subarea N3
CHEMICAL (
Dichtorodrfluoromethane
Dichloroethane. 1.1- (Elhylidene dichloride)
Dlchloroethane. 1.2-
Dlchloroethene, 1,1- (Vinyhdine chloride)
Dlchloroethene (trans). 1 .2-
Dichtorophenol, 2,4-
Dichkttopropane. 1 ,2- (Propylane dichloride)
Dlchloropropana (els). 1 .3-
Dichloropfopene (trans). 1 ,3-
Diathylphthalata
Dimethoxybenzidln*. 3.3'-
Dlmathylphenot, 2,4-
Uimettiyiphthaiate
Dl-n-butylphthalate
Dinitrotoluene. 2.6-
Ornttro-2-mvttiylphanol, 4.6-
DinHrophanol, 2,4-
DinMrotoluane, 2,4
Dioxana, 1,4-
Di(n)octyl phthalate
D.2.4-
Ethyl mathacrylala
Ethylb«nzena
Fthylana dibromida
Ethylene oxide
Ethylene thlourea
Fluoranthana
Fluorene
Formaldehyde
Furfural
Haptachlor
Haptachloroblphanyl
Haxachlorobanzana
Hexachloroblphenyl
Hexachlorobutadiene
Hexachlorocyclohaxana, gamma (Llndane)
Hexachlorocyclopentadierre
Hexachloroethan*
Hexachlorophene
Hexanona, 2-
lndeno(1 .2 ,3-cd)pyrane
Isophorone
Maleic hydrazide
Methoxychlor
Methyl t-butyt ether
Methyt-2-Penlanone. 4- (MIBK)
Methylene chloride
Methylnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nitroaniline, 2-
Nitroanilme. 3-
Inhalation
Slope
Factor
mg/kg-d)"-'
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
45E-02
NA
45E»00
NA
1 6E+00
NA
7 BE -02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0125
NA
0 007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RfD
(mg/kg-d)
1 4E-02
36E-02
NA
2 3E 03
50E-03
75E-04
29E-04
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
2 5E 02
25E-04
NF
50EO4
50E-04
NA
50E03
2 5E-03
2 3E 02
7 1E-02
1 4E-05
DA
20t 05
1 OE 02
1 OE 02
50E-02
36E 03
1 3E-04
NA
20E-04
NA
50E-05
75E-05
50E 06
2 5E-04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
57E 03
2 IE 01
NF
NA
IDE 02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E-04
3E-05
3E-05
3E-05
3E-05
55E-06
3E-05
3E-05
JE-O5
1 7E-05
1 2E-04
55E-06
55E-06
1 6E-05
55E-06
55E-06
55E-06
55E-06
4 9E-04
S5E-06
39E-05
25E-04
50E04
1 2E 04
3 IE-OS
1 5E-10
55E-06
67E-06
6 1E-04
55E-06
5 5E 07
1 4E 08
55E-06
1 4E 08
1 OE 04
5 5E 05
55E 06
55E-06
3 2E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
4 OE 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
NSavg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
NSavg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
NSavg
NSavg
N3 avg
NS avg
NSavg
NS avg
NSavg
NSavg
NS avg
f 13 avg
Off site
Vapor
Cone
(ug/mS)
59E 06
3 OE-07
3 OE-07
3 OE-07
30E 07
1 3E-07
3 OE-07
3 OE-07
3 OE-07
4 OE-07
2 BE -06
1 3E-07
1 3E-07
3 8E 07
1 3E-07
1 3E 07
1 3E-07
1 3E 07
1 2E-05
1 3E-07
93E-07
59E-06
12E05
28E-06
7 3E 07
35E-12
1 3E-07
1 6E 07
1 5E-05
1 3E-07
1 3E 08
34E-10
1 3E-07
34E-10
24E06
1 3E 06
1 3E 07
3E07
7E 07
5E 06
3E 07
6E 07
28E 06
1 3E 08
30E 07
30E 07
95E 06
1 OE 06
40E 10
1 3E 07
1 6E 07
! 6E 07
Cancer
Adult
Dose
(mg/kg-d)
2 IE 10
1 1E-11
1 IE-It
1 1E-11
1 IE-It
46E 12
1 1E-11
1 1E-11
1 1E-11
1 4E-11
97E-11
46E-12
46E-12
1 3E-11
46E-12
46E-12
46E-12
46E-12
42E 10
46E-12
33E-11
21E-10
42E-10
97E-11
26E-11
1 2E-16
46E-12
57E-12
5 1E-10
46E-12
46E 13
1 2E-14
46E-12
1 2E 14
85E-11
46E-11
46E 12
46E 12
27E It
54E 11
46E 12
57E 12
9 7E 11
46E 13
1 IE 11
1 IE 11
3 3E 10
S5E 11
1 4E 14
46E 12
5 7E 12
5 7E 12
Cancer
Child
Dose
(mg/kg-d)
52E-10
26E 11
26E 11
26E-11
26E-11
1 2E-11
26E-11
26E-11
26E-11
35E-11
24E-10
2E-11
2E-11
3E-11
2E-11
2E-11
2E-11
1 2E-11
10E-09
1 2E-11
82E-11
52E-10
1 OE 09
24E-10
64E-11
3 IE 16
1 2E-11
1 4E-11
1 3E-09
1 2E-11
1 2E-12
29E-14
1 2E-11
29E-14
2 1E-10
1 2E-10
1 2E-11
1 2E 11
67E It
1 4E 10
1 2E 11
1 4E 11
24E 10
1 2E 12
26E 11
26E 11
8 3E 10
8 BE 11
35E 14
1 2E 11
1 4E 11
1 4E 1 1
Cancer
School-age
Dose
(mg/kg-d)
3 1E 10
6E 11
6E 11
6E 11
6E-11
70E 12
6E-11
6E-11
6E-11
2 1E-11
1 5E-10
70E-12
70E-I2
20E-11
70E-12
70E-12
70E-12
70E-12
63E-10
70E-12
49E-11
31E-10
63E-10
1 5E-10
39E-11
t 9E-I6
70E-12
85E-12
77E-10
70E-12
70E-13
1 8E-14
70E-12
1 BE 14
1 3E-10
70E-11
70E 12
70E-12
4 IE-It
82E It
70E 12
85E 12
1 5E 10
70E IS
1 6E 11
1 6E 11
50E 10
53E 11
2 IE 14
70E 12
BSE 12
85E 1?
Cancer
Farmer
Dose
(mg/kg-d)
46E 10
23E 11
23E 11
23E 11
23E-11
1 OE-11
23E-11
23E 11
23E 11
32E-11
22E 10
1 OE-11
tOE-tt
29E-11
1 OE-11
lOE-tt
t OE 11
10E 11
93E-10
1 OE-11
73E-11
46E-10
94E-10
226-10
57E 11
27E-16
1 OE-11
13E 11
1 1E-09
1 OE-11
10E-12
26E-14
1 OE-11
26E-14
1 9E-10
1 OE 10
1 OE 11
1 OE-11
60E 11
1 2E 10
1 OE 11
1 3E 11
22E 10
1 OE 12
23E 11
2 3E 11
7 IE 10
7 BE 11
3 IE 14
1 OE 11
1 3E 11
t 3F 11
Noncancer
Adult
Dose
(mg/kg-d)
1 6EO9
82E 11
82E 11
82E-11
82E-11
36E-11
82E-11
82E-11
82E-11
1 IE 10
76E-10
36E 11
36E-M
t OE-10
36E-11
36E-11
36E-11
36E-11
32E-09
36E-11
26E-10
16E-09
33E09
76E-10
20E 10
96E-16
36E-11
44E 11
40E09
36E-11
36E-12
92E 14
36E 11
92E 14
66E 10
36E 10
36E-11
36E 11
2 IE 10
42E 10
36E 11
44E 11
76E 10
36E 12
82E 11
82E 11
26E 09
2 7E 10
1 IE 13
36E 11
4 4E 11
44F II
Noncancer
Child
Dose
(mg/kgd)
60E 09
3 IE 10
3 IE 10
31E-10
31E-10
1 4E-10
31E-10
31E-10
3 1E-10
4 1E-10
2 BE -09
1 4E-10
1 4E-IO
38E-10
1 4E-10
1 4E-10
t 4E-10
1 4E-10
1 2E-OB
,14E-10
95E-10
60E-09
t 2E-08
2 BE -09
75E-11
36E 15
1 4E-10
t 6E-10
1 5E 08
1 4E 10
1 4E It
34E 13
1 4E 10
34E 13
2 5E 09
1 3E 09
1 4E 10
1 4E 10
79E 10
1 6E 09
1 4E 10
1 6E 10
2 BE 09
1 4E 11
3 IE 10
3 IE 10
9 7E 09
1 OE 09
4 IE 13
1 4F 10
1 6E 10
! r,f to
Noncancer
School-age
Dose
(mg/kg-d)
36E09
1 9E 10
19E 10
1 9E-10
1 9E-10
82E-11
t 9E-10
t 9E-10
t 9E-10
25E-10
1 7E-09
82E-11
82E 11
23E-10
B2E-11
B2E-11
B2E-11
82E-11
73E-09
B2E-11
5 BE 10
36E09
74E09
1 7E-09
45E-10
22E 15
B2E-11
99E-11
90E 09
82E 11
82E 12
2 IE 13
82E-11
2 IE 13
1 5E 09
8 IE 10
B2E 11
82E 11
47E 10
95E 10
B2E 11
99E 11
1 7E 09
82E 12
1 9E 10
1 9E 10
59E 09
62E 10
25E 13
82E 11
99E 11
99E 11
Noncancer
Farmer
Dose
(mg/kg-d)
1 6E 09
B2E 11
82E II
82E 11
82E-11
36E-11
82E-11
B2E It
82E-11
1 1E-10
76E 10
36E 11
36E It
t OE-10
36E-11
36E-11
36E-11
36E-11
32E-09
36E-11
26E 10
16E49
33E09
76E-10
20E-10
96E 16
36E 11
44E-11
40E-09
36E 11
36E 12
92E 14
36E 11
92E 14
66E-10
3 BE 10
36E 11
36E 11
2 IE 10
42E 10
36E 11
44E 11
76E 10
36E 12
82E 11
82E 11
26E 09
2 7E 10
1 IE 13
3 BE 11
44E 11
44F 1 1
/olume V. Appendix V-14
-------
TABl E 6  Average tnhalatton Risks and f Joncancor HQs m Subatea
CHEMICAL
Dichlorodlnuotomethane
Dichloroelhane. 1.1- (Elhylidene dichlonde)
Dichlotoethane. 1,2-
Dichloroettiene, 1.1- (Vinylidine chloride)
Dichloroethene (tram), 1 ,2-
Dichlorophenol. 2.4-
Dichloropropane. 1 ,2- (Propylene bichloride)
Dichloiopropene (cis). 1 .3
Dichloropropene (trans), 1 ,3-
Diethylphthalate
Dimethoxyberuldine. 3,3
Dlmethylphenol, 2,4-
Dimethylphthalata
Di-n-butytphthalate
Dinrtrotoluene, 2,6-
Dlnttro-2-methylphenol. 4,6-
Dinrbophenol. 2.4-
Dlnrbotoluene. 2.4-
Oioxane. 1 .4-
Di(n)octy< phthalate
D. 2.4-
Ethyl methacrylate
Ethyl benzene
Ethylene dibromide
Ethylene oxide
Ethylene thiourea
Fluoranthene
Fluor ene
Formaldehyde
Furfural
Heptachlor
Heptachlorobiphenyl
Hexachlorobenzana
Hexachloroblphenyl
Hexachlorobutadiene
Hexachlorocyclohexane, gamma (Lindane)
Hexschlorocyclopentadiene
Hexachloroethane
Hexachlorophene :
Hexanone, 2-
Indenofl ,2,3-cd)pyren«
Isophorone
Maleic hydrazide
Methoxychtor
Methyl-t-butyl ether
Methyl-2-Pentanone. 4- (MIBK)
Methylene chloride
Methylnaphthalene, 2-
Monochlorobiphenyl
Naphthalene
Nrtioamlme 2-
Nrtroaniline 3-
Inhalation
Slope
Factor
(mg/kg-d)"-1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E 01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
4 5E 02
NA
45E+00
NA
1 6E*00
NA
7 BE -02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA.
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
0 25
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
OOO005
HF
Inhalation
RfD
(mg/kg d)
1 4E 02
36E 02
NA
23E 03
50E-03
75E 04
29E 04
1 4E 03
1 4E-03
20E-01
NA
50E-03
NA
25E 02
25E-04
NF
50E 04
50E-04
NA
50E 03
25E 03
2 3E 02
7 IE 02
1 4E-05
NA
20E 05
1 OE 02
1 OE 02
50E4)2
36E-03
1 3E-04
NA
20E 04
NA
50E 05
75E-05
50E-06
2 5E-04
7 5E-05
NF
NA
50E 02
1 3E-OI
1 3E 03
2 IE 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E-05
NF
Emission
Rate
(g'sec)
2 5E 04
3E 05
3E 05
3E 05
3E 05
55E 06
3E 05
3E 05
3E 05
7E 05
2E 04
55E-06
55E 06
1 6E 05
55E 06
55E 06
55E 06
55E 06
49E 04
55E 06
3 9E-05
25E 04
50E 04
1 2F 04
31E-05
1 5E-10
55E 06
67E-06
6 1E-04
55E-06
55E 07
1 4E-08
55E-06
1 4E-08
1 OE 04
55E-05
55E-06
55E-06
3 2E 05
6 4E 05
55E 06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
N3avg
N3avg
N3 avg
N3avg
f ,13 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3*vg
N3avg
N3avg
N3svg
N3avg
N3avg
N3«vg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
; N3 avg
' tJ3 avg
N3 avg
H3avg
N3avg
tJ3 avg
U3avg
N3 avg
N3avg
N3 avg
TJ3 avg
Adult
Cancel
Risk
NT
NT
96E 13
1 3E-11
NT
NT
NT
1 4E 12
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
74E-11
90E-12
NT
NT
NT
2 3E-11
NT
2 1E-12
NT
75E-12
NT
67E-12
NT
NT
65E-14
NT
NT
NT
NT
NT
NT
NT
NT
55E 13
NT
HT
NT
NT
m
Child
Cancer
Risk
NT
NT
24E-12
32E 11
NT
NT
NT
34E 12
34E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
22E-11
NT
NT
NT
58E-11
NT
52E-12
NT
1 9E-11
NT
1 7E-11
NT
NT
1 6E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 4F_ 12
NT
NT
NT
NT
Ml
School age
Cancer
Risk
NT
NT
1 4E 12
19E 11
NT
NT
NT
2 1E 12
2 IE 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E 10
1 4E-11
NT
NT
NT
35E-11
NT
31E-12
NT
1 1E-11
NT
10E-11
NT
NT
98E-14
NT
NT
NT
NT
NT
NT
rjr
NT
8 3F 13
NT
NT
(IT
in
til
F aimer
Cancer
Risk
NT
NT
2 IE 12
28E-11
NT
NT
NT
30E 12
30E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E 10
20E-11
NT
NT
NT
5 IE It
NT
46E-12
NT
1 7E-11
NT
1 5E-11
NT
NT
1 4E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 2F 12
m
NT
NT
NT
m
                                                                                                                                              Adult      Child   School age   Faimel
                                                                                                                                            Noncancer Noncancer Noncancer Noncancer
                                                                                                                                               HQ       HQ       MQ       HQ
1 1E 07
23E 09
NT
37E 08
1 6E 08
4 BE 08
29E 07
5 8E-08
5 BE 08
55E-10
NT
72E-09
NT
4 1E-09
1 4E^)7
NT
72E 08
72E08
NT
72E-09
1 OE-07
72E4»
46E-08
53E05
NT
48E-11
36E4»
44E09
80E08
1 OE 08
2 9E-08
NT
1 8E 07
NT
1 3E 05
4 BE 4)6
72E-O6
1 4E-07
28E06
NT
NT
B8E-10
60E 09
29E 09
3BE 10
1 4E 08
t 2F 08
NT
NT
36E 09
3 IT 06
HI
42E 07
86E 09
NT
1 4E 07
6 IE 08
1 BE 07
1 IE 06
2 IE 07
2 IE 07
2 1E 09
NT
2 7E-08
NT
1 5E 08
54E 07
NT
2 7E 07
2 7E 07
NT
27E 08
3 BE 07
2 7E 07
1 7E 07
2 OE-04
NT
1 8E 10
1 4E 08
1 BE 08
30E 07
3 BE 08
1 IE 07
NT
6 BE 07
NT
50E 05
1 BE 05
2 7E 05
54E07
1 OE 05
NT
NT
33E 09
23E 08
1 IF 08
1 4E 09
5 4F OB
4 r>T 08
111
NT
1 41. 08
1 2F Or>
tl!
25E07
52E-09
NT
82E08
3 7E 08
1 IE 07
65E07
1 3E 07
1 3E 07
1 3E 09
NT
1 6E-OB
NT
93E09
33E-07
NT
1 6E 07
1 6E-07
NT
16E08
2 3E 07
1 6E 07
1 OE 07
1 2E 04
NT
1 IE 10
82E 09
99E 09
1 BE 07
23E 08
6 5E-08
NT
4 1E 07
NT
30E 05
1 IE 05
1 6E 05
33E 07
6 3E 06
NT
fJT
2 OE 09
1 4E_ 08
6 5E* 09
8 7E 10
32E 08
2 ?r 08
NT
NT
82E 09
7 OF. 06
HI
1 IE 07
2 3E 09
NT
3 7E 08
1 6E 08
4 BE 08
29E 07
5 BE 08
58E 08
55E-10
NT
72E09
NT
4 IE 09
1 4E-07
NT
72E 08
72E-08
NT
72E 09
1 OE 07
72E 08
46E 08
53E 05
NT
48E 11
36E 09
44E 09
60E 08
10E 08
29E 08
NT
1 8E 07
NT
1 3E 05
48E 06
72E 06
1 4E 07
2 BE -06
NT
NT
BBE 10
60E 09
29E09
3 BE 10
1 4E OB
1 2E 08
NT
NT
3 6E 09
^ IF 06
tIT
/olume V Appendix V '*
-------
TABLE 6  Average li
                 Inhaiation
                         Risks and Noncancer HQs in Subarea N3
CHEMICAL
Nitroaniline, 4-
Nrttobenzene
NHrophenol, 2
Nilrophenol, 4-
N Nitroso-dl-n butylamine
N-Nrtroso-dl-n-propylamlne
N-Nttrosodiphanylamfne (Diphenylamrne)
Nonechloroblphenyl
Octachlorobiphenyl
Pentochlofobenzene
Pentachloroblphenyl
Pentachtoronrbobflnzene
Pentachlorophenol
Phenanthrene
Phenol
Pyiene
Safrole (5-(2-PropenyO-1 ,3-benzodloxole)
Styrene
Tetrachloroblphenvl
Tetrachloroelhane. 1.1.1,2-
Tetrachloroettiane. 1.1.2.2-
T etrachlof oethene
Telrtchlofoph.no). 2,3.4,6-
Toluene
TrlchlofO-1.2.2-lrinuofoethane. 1.1.2-
Trlchlorobenzene. 1,2,4-
Tfkhloroblphenyl
Trichlotoethane. 1.1.1- (Methyl chloroform)
Trtchloroethane. 1.1.2-
Trfchlor oethene
Trichlorofluoromethane
Trichlorophenol. 2,4.5-
Trlchlorophenol. 2,4.8-
Vlnyl acetate
Vinyl chloride
Xylan*, m/p- (m/p-Dimethyl benzene)
Xylene, o- (o-Dimethyl benzene)
2.3.7.8-TCDD
1.2.3,7.8-PCDO
1.2.3.4.7.8-HxCDD
1.2.3.6.7.8-HXCDO
1. 2.3,7.8.9 HxCDO
1.2.3.4.6.7.8-HpCDD
OCDO
2.3.7,8-TCDF
1.2.3.7.8-PCDF
2,3,4. 7.8 PCDF
12347 8 HxCDF
1.2.367.8 HxCDF
2.3.4.6.7.8 HxCDF
Inhalation
Slope
Factor
(mg/kgd)»-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
IDE -02
NA
30E-01
NA
NA
15E+05
75E+04
1 5E»04
1 5E+04
5E»04
5E+03
5E+02
5E»04
5E«03
5E+04
5E»04 '
5E«04
1 5E«04
RAC
(mg/m3)
NF
OOOOS
NF '
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02825
NA
000875
002625
01
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RtTJ
(mg/kg-d)
NF
1 4E-04
. NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E^)3
NA
1 5E 01
75E-03
NF
7 1E-02
NA
75E-03
NA
2 5E 03
7 5E-03
2 9E-02
2 1E»00
1 4E-02
NA
7 IE 02
10E-03
NA
50E-02
2 5E-02
NA
1 4E-02
NA
5 OE 01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E-06
55E-06
1 2E-04
67E-06
67E-06
14E-08
1 4E-08
48E-05
1 4E-08
34E-05
55E-06
87E-06
55E-08
55E-08
1 2E-04
23E^B
1 4E-08
55E-06
55E-06
5 IE-OS
6 BE -06
6 1E-04
33E^M
55E-08
30E-08
13E-05
13E-05
196-05
25E44
S5E-06
55E06
64E-05
2 5E-04
38E-04
55E-06
1 08E-11
678E-1I
895E-11
1 66E 10
1 09E 10
1 24E 09
6 I5E-09
877E-11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
N3avg
N3«vg
N3avg
N3avg
N3avg
N3avg
NSavg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3»vB
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
M3 avg
N3avg
N3 avg
N3 avg
N3 avg
N3 avg
N3 avg
N3 avg
N3 avg
N3avg
Off-site
Vapor
Cone
(ug/m3)
1 6E 07
1 3E-07
1 6E-07
1 3E-07
29E-06
16E-07
1 6E-07
34E-10
34E-10
1 1E-06
34E-10
81E-07
13E-07
1 6E-07
1 3E-07
1 3E4I7
2 BE -08
54E-07
34E-10
3E^>7
3E-07
2E«
6E07
5E-05
79E-06
13E-C7
73E-10
30E-07
30E^)7
45E-07
59E-06
1 3E-07
1 3E-07
1 5E-06
59E-06
91E-06
1 3E-07
26E-13
1 6E-12
2 IE 12
40E 12
26E 12
30E-11
1 5E 10
2 IE 12
83E 12
1 1E 11
34E 11
32E 11
36E-11
Cancer
Adult
Dose
(mg/kg-d)
57E-12
46E-12
57E-12
46E-12
1 OE-10
57E-12
57E-12
1 2E-14
1 2E-14
40E-11
1 2E-14
28E-11
46E-12
5 7E-12
46E-12
46E-12
97E-11
19E-11
1 2E-14
46E-12
46E-12
43E-11
57E12
52E-10
2 8E-10
46E-12
26E-14
1 1E-11
1 1E-11
16E-11
2 1E-10
46E-12
46E-12
54E-11
2 1E-10
32E-10
46E-12
9 IE 18
57E-17
76E-17
1 4E-16
92E 17
1 OE 15
52E 15
74E 17
29E 16
39E 16
1 2E 15
1 IE 15
1 3E 15
Cancer
Child
Dose
(mg/kg-d)
1 4E-11
12E-11
14E-11
12E-11
25E-10
1 4E 11
14E-11
29E-14
29E-14
1 OE 10
29E-14
71E-11
12E-11
1 4E-11
12E-11
1 2E-11
24E-10
47E-11
29E-14
12E-11
12E 11
1 1E-10
1 4E-11
1 3E-09
6 9E-10
12E-11
64E-14
26E 11
26E-11
39E-11
52E-10
1 2E-11
12E-11
1 4E-10
52E-10
8 OE-10
1 2E-11
23E-17
1 4E 16
1 9E 16
35E-16
23E 16
26E 15
1 3E 14
1 BE 16
7 3E 16
98E 16
30E 15
2 BE 15
32E 15
Cancer
School-age
Dose
(mg/kg-d)
85E-12
70E-12
85E-12
70E-12
1 5E-10
85E-12
85E-I2
1 8E-14
1 8E-14
6 IE 11
1 BE 14
43E-I1
70E-12
8 5E-12
70E-12
70E-12
1 5E-10
29E-11
1 8E-14
70E-12
70E 12
65E-11
87E-12
78E-10
42E-10
70E-12
3 BE 14
16E-11
1 6E 11
24E M
31E-10
70E-12
70E-12
82E-11
3 1E-10
48E-10
70E-12
14E-17
86E 17
1 1E-16
2 IE 16
1 4E 16
1 6E-15
78E 15
1 IE 16
44E 16
59E 16
1 BE 15
1 7E 15
1 9E 15
Cancer
Farmer
Dose
(mg/kg-d)
1 3E-11
10E-11
1 3E-11
10E 11
23E-10
13E-11
136-11
26E-14
26E-14
89E-11
26E-14
6 3E-1 1
10E-11
13E-11
10E-11
1 OE-11
22E-10
42E-11
26E-14
1 OE-11
1 OE-11
96E-11
1 3E-11
12E-09
62E-10
1 OE-11
57E-14
23E-11
23E-11
35E-11
46E-10
1 OE-11
1 OE-11
1 2E 10
46E-10
71E-10
1 OE-11
20E-17
1 3E-16
1 7E-16
3 IE 16
20E 16
2 3E 15
1 2E 14
1 6E 16
65E 16
8 BE 16
2 7E 15
25E 15
2 8F 15
Noncancer
Adult
Dose
(mg/kg-d)
44E-11
36E 11
44E-11
36E-11
8 OE-10
44E-11
44E-11
92E-14
92E14
31E-10
92E 14
22E-10
36E-11
44E-11
36E-11
36E-11
76E-10
1 5E-10
92E-14
36E-11
36E-11
34E-10
45E-11
40E09
22E-09
36E-11
20E-13
82E 11
82E-11
1 2E-10
16E09
36E-11
36E-11
42E-10
16E09
25E-09
36E-11
71E 17
45E-16
59E-16
1 IE 15
72E 16
82E 15
40E 14
5 BE 16
23E 15
3 IE 15
94E 15
8 BE 15
99F. 15
Joncancet
Child
Dose
(mg/kg-d)
16E 10
14E-10
16E-10
1 4E-10
30E-09
1 6E-10
16E-10
34E-13
34E-13
12E-09
34E-13
83E-10
1 4E-10
1 6E-10
1 4E-10
1 4E-10
2 BE -09
55E-10
34E-13
1 4E-10
1 4E-10
13E-09
1 7E-10
15E-08
61E-09
1 4E-10
74E 13
31E-10
3 IE 10
46E 10
60E-09
1 4E 10
1 4E-10
16E-09
60E09
93E09
1 4E 10
27E 16
1 7E 15
22E 15
4 IE 15
2 7E 15
30E 14
1 5E 13
22E 15
BSE 15
1 IE 14
35E 14
33E 14
3 7E 14
Noncancer
School age
Dose
(mg/kgd)
99E 11
82E-11
99E 11
82E 11
1 8E-09
99E-11
99E-M
21E-13
2 1E-13
71E-10
2 1E-13
5 OE-10
62E-11
99E 11
82E-11
82E-11
17E-09
33E-10
2 IE 13
82E-11
82E-11
76E-10
1 OE-10
9 1E-09
49E-09
62E-11
45E 13
19E 10
19E-10
28E 10
36E09
82E-11
82E 11
95E 10
36E09
56E-09
B2E-11
1 6E 16
1 OE 15
13E 15
25E 15
16E 15
1 BE 14
- 9 IE 14
1 3E 15
5 IE 15
69E 15
2 IE 14
20E 14
2?E 14
Noncancer
Farmer
Dose
(mg/kg-d)
44E-11
36E-11
44E 11
36E 11
8 OE-10
44E 11
44E-11
92E-14
92E 14
31E-10
92E-14
22E-10
36E 11
44E-11
36E-11
36E-11
76E-10
1 5E-10
92E 14
36E 11
36E 11
34E-10
45E11
40E09
22E09
36E-11
20E13
62E-11
82E 11
1 2E-10
1 6E 09
36E11
36E-11
42E 10
16E-09
25E09
36E-11
7 IE 17
45E-16
59E 16
1 IE 15
72E 16
82E 15
40E 14
5 BE 16
23E 15
3 IE 15
94E 15
8 BE 15
99F 15
Volume V. Appendix V-14
-------
TAB! E 6  Average Inhalation Rr ks ana1 f Jonc.inrpr HQs in Suhaio.i N1
CHEMICAL
Nitioanlline. 4-
Nitiob«nz«n«
Nitrophenol. 2-
Nitiophenol. 4-
N Nitroso-di-n-butylannine
N Nrtroso-dl n-piopylamlne
N Nitrosodiphanylamine (Diphenylamme)
Non»chloioblpheny1
Octachlotobiphenyl
Pentachlorobenzana
Pentachloiobiphenyt
PentachlotonHiobenzene
Pentachkxophenol
Phenanlhrene
Phenol
Pyrene
Sahole (5-(2-Propenyl) 1.3 benzodioxole)
Slytene
Tebachloiobiphenyl
Tebachloroelhane. 1,1,1.2
Tebachloioethane. 1. 1.2.2-
Tebachlofoethene
Tetoachlotophenol. 2,3.4.6-
Toluene
Ttichloto- 1 .2 .2 tllfluoeoethane . 1.1.2-
Tilchloroberuene. 1,2.4-
Trichloroblphenyl
Ttichloroelhane. 1,1,1- (Methyl chlorofoim)
Trlchlofoethane. 1.1,2-
Trlchloroethene
TrichloroDuoromethane
Trchlorophenol, 2.4.5-
Trlchloiophenol. 2,4,6-
/inyt acetate
/inyl chloride
CDD
3.7.8 TCDF
2 3 7.8 PCDF
34 7. 8 PCDF
,234.78HxCOF
23678 M«CDF
34678 H«CDF
Inhalation
Slope
Factor
(mg/kg d)»-1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2664)2
20E 01
70E-03
HA
NA
NA
NA
NA
NA
57EO2
60E 03
NA
NA
1 OE-02
NA
3 OE-01
NA
NA

1 5E+05
75E*04
1 5E+04
1 5E+04
1 5E+04
1 5E»03
1 5E«02
1 5E»04
7 5E»03
7 5E«04
1 5E+04
1 5E*04
1 5E*04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
002625
01
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg d)
NF
1 4E 04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E04
7 5E-03
NA
1 5E 01
7 5E-03
NF
7 IE 02
NA
75E 03
NA
25E 03
7-5E-03
29E 02
2 1E»00
1 4E 02
NA
7 IE 02
1 OE 03
NA
50E 02
2 5E-02
NA
1 4E-02
NA
50E 01
5 OE-01

NA
NA
NA
NA
NA
HA
NA
NA
UA
NA
NA
NA
NA
Emission
Rale
(B/sec)
67E 06
55E 06
6 7E 06
55E 06
1 2E-04
67E 06
67E-06
1 4E 08
t 4E 08
48E05
1 4E 08
34E05
55E06
67E 06
55E06
55E06
1 2E 04
23E05
1 4E 08
55E06
55E06
51E05
6 6E 06
6 IE 04
33E 04
55E 06
30E-08
1 3E 05
1 3E 05
19E-05
2 5E 04
55E 06
55E 06
64E05
25E 04
38E 04
55E-06

1 08E-11
678E 11
895E-11
1 66E-10
1 09E 10
1 24E 09
615E 09
877E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subaiea
N3 avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3ivg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3 avg
N3avg
N3 avg
N3 avg
N3 avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
143 avg
N3avg
N3avg

N3avg
N3 avg
H3 avg
fJ3 avg
N3avg
N3avg
t)3 avg
113 avg
113 avg
143 avg
N3 avg
tn avg
f n avg
Adull
Cancel
Risk
NT
NT
NT
NT
55E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 13
94E 13
88E-14
NT
NT
NT
NT
NT
NT
60E-13
94E-14
NT
NT
46E-14
NT
62E-11
NT
NT

1 4E 12
43E 12
1 1E-12
2 1E-12
1 4E 12
1 6E 12
78E 13
1 1E-12
2 2E 12
30E 11
1 BE 11
1 7E 11
1 9E 1 1
Child
Cancer
Risk
NT
NT
NT
NT
1 4E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E 13
24E 12
22E 13
NT
NT
NT
NT
NT
NT
1 5E 12
23E-13
NT
NT
1 2E-13
NT
1 5E-10
NT
NT

34E-12
1 IE 11
2 BE 12
52E 12
34E 12
39E 12
1 9E 12
2 BE 12
54E 12
74E 11
45E 11
42E 11
48E-11
School age
Cancer
Risk
NT
NT
NT
NT
83E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 8E 13
1 4E 12
1 3E 13
NT
NT
NT
NT
NT
NT
9 IE 13
1 4E-13
NT
NT
70E-14
NT
94E-11
NT
NT

2 IE 12
65E-12
1 7E 12
32E 12
2 IE 12
24E 12
1 2E 12
1 7E 12
33E 12
45E 11
2 7E 11
25E 11
29E 11
Faimer
Cancel
Risk
NT
NT
NT
NT
1 2E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
27E 13
21E-12
20E-13
NT
NT
NT
NT
NT
NT
1 3E 12
2 IE 13
NT
NT
10E-13
NT
1 4E-10
NT
NT

30E 12
95E 12
25E 12
47E 12
3 IE 12
35E 12
1 7E 12
25E 12
49E 12
66E 11
40E 11
38E 11
4 2F 11
                                                                                                                                               Adult      Child    School age   Faimer
                                                                                                                                             Noncancer Noncancei Noncancei Noncancer
                                                                                                                                                HQ       HO       HO       HQ
NT
2 5E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E-07
48E-09
NT
24E-10
4 BE -09
NT
2 1E-09
NT
4 BE -09
NT
1 3Efl7
60E09
1 4E 07
10E-09
25EO9
NT
12E09
8 2E 08
NT
3 2E 08
1 4E-09
NT
30E-08
NT
50E09
72E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
141
NT
NT
95E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 06
1 8E-08
NT
90E 10
1 8E-08
NT
77E-09
NT
1 BE-08
NT
50E07
22E08
5 3E 07
38E09
95E 09
NT
43E 09
3 IE 07
NT
1 2E 07
54E-09
NT
1 1E-07
NT
19E 08
2 7E 10
NT
NT
NT
NT
NT
NT
NT
III
UT
NT
m
NT
III
NT
5 7E 07
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 7E-07
1 IE-OS
NT
54E-10
1 IE-OS
NT
47E-09
NT
1 IE-OS
NT
30E 07
1 3E 06
3 2E 07
23E-09
5 7E 09
NT
26E 09
1 9E 07
NT
73E 08
33E 09
NT
6 7E-08
NT
1 IE 08
1 6E 10
NT
tJT
NT
NT
NT
NT
NT
m
NT
Nt
NT
NT
NT
NT
2 5E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 OE-07
48E-O9
NT
24E 10
4 BE -09
NT
2 1E-09
NT
4 BE -09
NT
1 3E4)7
60E-09
1 4E4J7
1 OE 09
25E4W
NT
1 2E09
8 2E-08
NT
32E 08
1 4E-D9
NT
30E-09
NT
50E-09
72E 11
NT
NT
NT
NT
NT
NT
NT
NT
III
Nt
m
NT
NT
 jlums V Appendix V-1*
                  n
-------
                 Inn.
TABLE 6  Average Inharation Risks and Noncancei HOs in Subaiea N3
CHEMICAL
1.2,3.7.8.9-HxCDF
123467 8 HpCDF
1. 2.3,4.7.8.9 HpCDF
OCDF
Oloxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavatent)
Chromium (trivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Tola! nitrogen oxides (NOx)
Total sulfur o»tde-s (SOx)
Paniculate matter
Resplrable particulales
Inhalation
Slope
Factor
(mg/kg-d)A-1
1 5E»04
1 5E+03
1 5E+03
1 5E»02

MA
MA
SO
NA
64
61
41
NA
NA
NA
NA
064
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000436
0004375
0875
NA
NA
0000075
00175
0004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfO
(mg/kg-d)
NA
NA
NA
NA

NA
10E-O4
75E-05
36E-05
t 3E-03
136-04
1 3E-03
25E-01
NA
NA
2 IE 05
50E-03
1 3E-03
13E-03
18E-05
75E-02
5DE-04
NA
NA
NA
NF
Emission
Rale
(g/sec)
293E-10
930E 09
1 22E 09
1 89E 08
4 28E-08
2 4E-04
42E-06
37E-05
1 5E-04
33E-06
16E-05
71E-07
7 1E-07
94E05
43E-05
t 4E-03
SOE-06
4 7E-04
15E^)5
34E-05
1 2E-04
3 2E-02
24E+00
91E-02
7 2E-02
7 2E-02
Subaiea
N3avg
N3avg
N3avg
N3avg

N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
Off-site
Vapor
Cone
(ug/m3)
70E-12
2 2E-10
29E 11
45E-10
1 OE-09
56E-03
1 OE 07
89E-07
36E-06
79E-10
3 6E-07
1 7E 08
1 7E-08
23E06
1 OE 06
34E-05
1 2E-07
1 IE-OS
36E07
82E-07
29E-06
77E-04
5 BE 02
2 2E 03
1 7E 03
1 7E-03
Cancer
Adull
Dose
(mg/kg-d)
25E 16
79E-15
1 OE 15
1 6E-14
36E-14
20E-10
35E-12
31E-11
1 3E-10
26E-14
1 4E-11
60E-I3
60E-13
79E-11
36E-11
12E-09
42E-12
40E-10
1 3E-11
29E-11
10E-10
27E-08
20E-06
77E-08
61E-08
61E-08
Cancer
Child
Dose
(mg/kgd)
62E-16
20E-14
26E 15
40E 14
90E-14
51E-10
8 BE 12
76E-11
32E-10
69E-14
34E-11
1 5E-12
1 5E-12
20E-10
91E-11
29E09
1 1E-11
99E-10
3 2E-1 1
72E-M
2 5E-10
6 7E-06
51E-06
1 9E-07
1 5E-07
1 5E-07
Cancer
School-age
Dose
(mg/kg-d)
37E-16
1 2E-14
16E 15
24E-14
54E-14
31E-10
53E-12
47E-11
1 9E-10
42E-14
20E-11
90E-13
90E-13
t 2E-10
55E-11
18E-09
64E-12
60E-10
19E-11
43E-11
1 5E-10
4 IE 08
3 IE 06
1 2E-07
92E48
92E-08
Cancer
Farmer
Dose
(mg/kg-d)
55E-16
1 7E-14
23E-15
36E 14
80E-14
45E-10
79E-12
69E-11
28E-10
62E-14
30E 11
1 3E-12
1 3E-12
1 8E-10
8 IE 11
26E-09
94E-12
88E-10
26E-11
64E-11
2 3E-10
60E-08
45E-06
1 7E 07
1 4E-07
1 4E-07
Noncancer
Adult
Dose
(mg/kg-d)
19E-15
61E-14
80E-15
1 2E-13
28E-13
16E-09
28E-11
24E-10
99E-10
22E-13
1 1E-10
47E 12
47E-12
62E-10
2 BE 10
92E-09
33E-11
31E-09
99E-11
22E 10
79E-10
2 IE 07
16E-05
60E-07
47E-07
4 7E-07
Noncancer
Child
Dose
(mg/kg-d)
72E 15
23E-13
30E-14
4 7E-13
1 1E-12
59E-09
1 OE-10
91E-10
37E-09
8 IE 13
39E-10
1 7E-11
1 7E-11
23E-09
1 1E-09
3 4E-08
1 2E-10
1 2E-08
37E 10
84E-IO
29E-09
79E07
5 9E-05
22E-06
18E06
1 BE -06
Noncancer
School-age
Dose
(mg/kgd)
43E-15
1 4E-13
1 8E-14
2 BE 13
63E-13
36E09
62E11
55E-10
22E-09
49E-13
2 4E-10
1 IE-It
1 1E-11
14E-09
64E-10
2 IE 08
74E-11
7 OE-09
22E 10
5 OE-10
1 8E-09
4 7E 07
3 6E-05
1 4E 08
1 1E-06
1 IE 06
Noncancei
Farmer
Dose
(mg/kgd)
19E-15
61E-14
80E-15
12E 13
28E-13
16E-09
28E-11
24E-10
99E 10
22E 13
1 1E-10
47E-I2
47E-12
62E-10
2 8E-10
92E-09
33E-11
3 IE 09
99E-11
2 2E-10
79E-10
21E4)7
16E05
60E-07
4 7E 07
4 7E-07
NOTES.
  NA - Not applicable
  NF * Not found      <:
  NT « No toxiciry Information
  HO - Hazard quotient
  HI  'HazardIndex
Volume V, Appendix V-14
-------
TABLE 6  Average Inhalation Rtsks and Noncancer MOs in Subarea N3
CHEMICAL
1 2 3.7.8,9 HxCDF
1 2.3.4.6.7.6 HpCDF
1,2.3.4. 7.8.9 HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Ars»nic
Barium
Ban/Ilium
Cadmium
Chiomium (hexavalenl)
Chromium (trivalenl)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
fine
tydfogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
'articulate matter
^esplrable particulales
Inhalation
Slope
Factoi
(mg/Vg d)A-1
t 5E»04
t 5E»03
1 5E«03
1 5E»02

NA
NA
50
NA
84
6 1
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
OOOOO6I
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E-05
1 3E 03
1 3E 04
1 3E 03
25E-01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E 03
1 8E 05
7 5E 02
50E-04
NA
NA
NA
NF
Emission
Rale
(g/sec)
293E 10
930E 09
1 22E-09
1 89E 08
428E-08
24E 04
42E-06
37E05
1 5E 04
3 3E 03
16E05
71E 07
7 IE 07
94E 05
43E 05
1 4E 03
50E06
4 7E-04
1 5E 05
34E05
1 2E 04
3 2E 02
24E*00
9 IE 02
7 2E 02
7 2E-02
Subaiea
N3 avg
N3avg
N3avg
N3avg

N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3avg
N3 avg
N3avg
N3avg
N3avg
N3avg
Adult
Cancel
Risk
3 7E 12
1 2E 11
1 5E 12
24E 12
1 2E 10
NT
NT
1 6E-09
NT
23E 13
82E 11
25E-11
NT
NT
NT
NT
35E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancel
Risk
93E 12
29E 11
39E 12
60E 12
30E 10
NT
NT
39E 09
NT
5 BE 13
2 IE 10
6 1E-11
NT
NT
NT
NT
88E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
56E 12
1 8E 11
2 3E-12
36E 12
1 BE 10
NT
NT
24E-09
NT
35E 13
1 2E 10
37E-11
NT
NT
NT
NT
53E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Fafmei
Cancer
Risk
83E 12
26E 11
34E 12
53E 12
26E-10
NT
NT
35E 09
NT
52E-13
1 8E 10
55E-11
NT
NT
NT
NT
79E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
 TOTES
  NA ° Not applicable
  NF = Nol found
  NT * No toxicity informarjbn
  HQ « Ha/ard quotient
  HI  = Hazard index
                                                                                Total Risk   26E-09   66E09    40E-09    59E-09
                                                                                                                                               Adult      Child    School age  Farmer
                                                                                                                                             Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                HQ       HQ       HQ        HQ
NT
NT
NT
NT
NT
NT
2 BE -07
32E-06
28E 05
1 7E-10
8 4E-07
37E-09
1 9E-11
NT
NT
4 3E 04
66E-09
25E06
79E08
1 3E 05
1 IE 08
4 2E 04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
10E06
1 2E 05
1 OE-04
65E-10
31E^)6
1 4E 08
70E-11
NT
NT
1 6E 03
2 5E-08
92E06
29E07
48E05
39E-08
16E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
62E 07
73E06
62E05
39E 10
1 9E 06
84E 09
42E-11
NT
NT
9 7E-04
1 5E 08
56E06
1 BE 07
29E05
2 4E 08
95E 04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E07
32E06
28E 05
1 7E-10
84E 07
37E 09
1 9E-11
NT
NT
4 3E 04
66E 09
25E06
79E08
1 3E 05
t 1E 08
4?E 04
NT
NT
NT
NT
                                                                                                                                    Total HI   10E-03   3 BE 03    2 3E 03    1 OE 03
  lume V. Appendix V 1 '
-------
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                                                                                                 &
-------
I ABLE 7  Aveiage Inhalation Risks and Noncancpi HOs m Subatea S1
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acelophenone
Acrylonitrile
Anthracene
Benzene
Benzole acid
Benzotrlchloride
Benzo(a)anthracene
Benzojajpyrene
Benzo(b)fluoranlhene
Benzo(g,h.l)perytena
Benzo(k)fluoranthene
Bis(2-chloroethoxy) methane
Bis(2-chlotoethyl)ether
Bls(2-chlorolsopropyl)ether
Blj(2 ethy1hexyt)phthalate
Bromodlchloromethane
Bromotbrm
Bromomethane
Bromodiphenyl ether p-
Butanone. 2- (Methyl ethyl ketone)
Butylberurylphthalate
Carbon disutfide
Carbon tetrachlorlde
Chlordane
Chloro-3 mettiylphenol, 4-
Chtoroanlllne, p- (4-Chloroanillne)
CMorobenzene
Chlorobenzilate
Chloroethane (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthalene. beta
Chlorophenol. 2-
Chlorodiphenyl ether, 4-
Chrysene *;
Cresol. m-
Crasol. o- (2-Methylphenol)
Cresol. p-
^rolonaldehyde
~umene
DDE. 4.4'-
3ibenr(a.h)anthracene
3ibromochloromethano
}ichloroben*ene. 1 3-
>chlorobenzene. 1 4
3ichlorobenzene. 1.2-
lichloiobenzidine. 3 3'
}ichlofobipheny1
Inhalation
Slop*
Factor
(mg/kg d)A-1
NA
NF
7 7E-03
NA
NA
2 4E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E«00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E 02
1 3E«00
NF
NA
NA
2 7E-01
NA
8 IE 02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RfD
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
2 5E 02
1 4E 04
75E 02
4 3E-04
1 OE»00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E 03
50E 03
36E 04
NA
7 1E 02
50E 02
7 1E 04
1 4E 04
1 5E 05
NF
1 OE 03
1 4E 03
50E 03
7 1E-01
2 5E 03
NA
2 OE 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
6 4E 04
NA
NA
50E-03
NA
5 7E 02
1 4E 02
NA
NA
Emission
Rale
(g'sec)
6 7E 06
67E 06
30E 04
29E 03
29E 04
20E 04
55E 06
1 5E 05
1 IE 05
32E-05
55E-06
55E 06
55E-06
55E-08
55E06
87E 06
t 3E 05
67E 06
37E^5
t OE 04
55E 06
49E 0<
67E 06
5 IE 05
55E-06
89E-05
1 6E^>4
5 5E-07
67E 06
67E 06
55E-06
37E 05
4 9E-04
2 7E 04
25E04
67E 06
55E 06
67E 06
55E 06
55E 06
55E-06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
3 3E 05
4 7E 08
Subaiea
S1 avg
SI avg
SI avg
SI avg
St avg
S1 avg
St avg
SI avg
SI avg
SI avg
SI avg
SI avg
St avg
St avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
St avg
SI avg
SI avg
S1 avg
S1 avg
St avg
SI avg
S1 avg
S1 avg
S1 avg
SI avg
SI avg
SI avg
SI avg
S1 avg
SI avg
SI avg
S1 avg
SI avg
S1 avg
; S 1 avg
SI avg
SI avg
SI avg
S 1 avg
St avg
SI avg
SI avg
St avg
S 1 avg
SI avg
Adult
Cancer
Risk
NT
NT
1 IE 11
NT
NT
24E 10
NT
2 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
72E 11
NT
NT
NT
1 OE 13
NT
NT
NT
NT
NT
4 IE 11
35E-12
NT
NT
NT
50E 11
NT
1 IE 10
76E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
fJT
nr
NT
rir
Child
Cancef
Risk
NT
NT
28E-11
NT
NT
59E-10
NT
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
NT
NT
NT
26E 13
NT
NT
NT
NT
NT
1 OE 10
87E-12
NT
NT
NT
1 2E-10
NT
26E-10
1 9E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
School age
Cancer
Risk
NT
NT
1 7E-M
NT
NT
36E-10
NT
32E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
1 6E-13
NT
NT
NT
NT
NT
62E 11
53E-12
NT
NT
NT
75E-11
NT
1 6E-10
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
KT
IIT
III
NT
Farmei
Cancer
Risk
NT
NT
25E It
NT
NT
53E-10
NT
4 7E 12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
23E-13
NT
NT
NT
NT
NT
91E 11
78E-12
NT
NT
NT
1 IE-10
NT
23E-10
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
tit
m
NT
IIT
m
NT
                                                                                                                                            Adult      Child   School age   Farmer
                                                                                                                                          Noncancei  Noncancer Noncancer Noncancer
                                                                                                                                             HQ        HQ        HQ       HO
1 7E-08
NT
1 8E 05
44E06
45E07
54E 05
2 BE 09
1 3E-06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
26E-08
2 9E-07
79E-07
42E08
53E05
NT
28E08
42E09
4 BE 06
42E 05
1 4E-06
NT
26E 07
1 5E 07
2 8E 07
26E-08
41E-06
NT
1 3E-08
1 7E^)7
NT
NT
1 7E 08
1 7E 08
1 7E 07
NT
33E-07
NT
NT
2 OF 07
NT
3 7f 09
1 V 08
NT
TIT
64E 08
NT
67E05
1 7E 05
1 7E 06
20E 04
1 IE 08
49E06
1 6E 09
NT
NT
NT
NT
NT
NT
NT
NT
96E 08
1 IE 06
30E4W
1 6E 07
20E-04
NT
10E07
1 6E 08
1 BE^W
16E04
53E-06
NT
96E 07
55E 07
1 IE 06
9 BE 08
1 5E-05
NT
4 BE 08
63E-07
NT
NT
63E 08
63E 08
63E 07
NT
1 ?F 06
NT
tit
7r.F 07
NT
1 Of 08
$ r,r m
in
nt
39E-08
NT
4 1E 05
1 OE 05
10E 06
1 2E 04
63E 09
30E 06
98E-10
NT
NT
NT
NT
NT
NT
NT
NT
58E48
64E417
18E-06
95E08
t 2E-04
NT
62E 06
95E09
1 IE 05
96E-05
32E-06
NT
58E 07
33E 07
64E 07
59E 08
92E 06
NT
29E 08
3 BE 07
NT
NT
3 BE 08
3 BE 08
3 BE 07
NT
74F. 07
NT
NT
4RT 07
NT
83F 09
3 IF 08
NT
ru
1 7E 08
NT
1 BE 05
44E 06
45E07
54E 05
2 BE 09
t 3E 06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
26E 08
29E07
79E 07
4 2E 08
53E-05
NT
2 BE 08
42E09
4 BE 06
42E 05
1 4E 06
NT
26E 07
1 5E 07
28E 07
26E 08
4 IE 06
NT
1 3E 08
1 7E 07
NT
NT
1 7E 08
1 7E 08
1 7E 07
NT
3 IE 07
NT
NT
2 OF 07
NT
3 7E 09
1 SE 08
NT
NT
olume V Appends V 14
-------
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-------
TABL E 7  Average Inhalation Risks and NoncancrM HQs in Sunarra SI
CHEMICAL
Dichlorodifluoromelhane
Dichlotoethane, 1.1- (Elhylidene dichloride)
Oichloroethana, t ,2-
Oichloroelhena, 1.1- (Vmylidine chloride)
Dichloroethene (trans). 1.2
Dichlorophenol, 2.4-
Dichloropropana. 1.2- (Propylene dichloride)
Dichloropropene (els), 1 .3-
Dichloropropene (trans). 1.3-
DielhylpMhalate
Dlmethoxybenzidine. 3.3'-
Dimethylphenol. 2.4-
Omattiylphthalata
Dt n-butylphthalate
Dinitrotoluene. 2.6-
CMnrbo-2-metfiylphenol. 4.6
Dinrtrophenol, 2.4-
Omitiotoluene. 2.4
Dionane. 1.4-
Dl(n)octy) phlhalate
D. 2.4-
Ethyl methacrylata
Ethylberuena
Ettiylene dibromide
Ethytene oxide
Elhytene thiourea
Fluor anthena
Fluorene
Formaldehyde
Furfural
Heptachlor
Heptachloroblphenyl
Haxachloiobanzena
Hexachlorobiphenyl
Haxachlorobutadiena
Hexachlorocyclohexane. gamma (Lindane)
Hexachlorocyclopentadiene
Hexachloro«(hana ,
Hexachlorophene
Haxanona, 2-
ndeno( 1 ,2 ,3-cd)pyiene
sophorone
vlaleic hydrazide
vlelhoxychlor
vlettiyl l-butyl ether
vlettiyt-2-Pentanone. 4- (MIBK)
vletbylene chloride
^ettiylnaphthalene. 2
^onochlorobiphenyl
Japhthalene
jitioanihne 2
Jitioamhne 3-
Inhalalion
Slope
Factor
(mg/kg d)*-1
NA
NA
9 IE 02
1 2E*00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
45E-02
NA
45E*00
NA
16E*00
NA
7 8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6£ 03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
0 75
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E-02
36E-02
NA
2 3E 03
50E 03
75E 04
2 9E 04
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
25E^)2
25E44
NF
50E 04
50E-04
NA
50E 03
25E 03
23E^)2
7 1E 02
1 4E^»
NA
20EX»
1 OE 02
1 OE 02
50E^>2
3 6E 03
1 3E-04
NA
20E04
NA
50E05
75E 05
50E 06
2 5E 04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E 05
NF
Emission
Rale
(g/sec)
25E 04
3E 05
3E-05
3E 05
3E 05
55E 08
3E05
3E-05
3E 05
1 7E-05
1 2E-04
55E06
55E 06
16E-05
55E08
55E 06
55E 08
55E-06
4 9E-04
55E^>6
39E05
2 5E 04
5 OE 04
1 2F 04
3 IE-OS
1 5E 10
55E 06
67E-06
6 IE 04
55E06
55E07
1 4E 08
55E-06
1 4E 08
1 OE-04
55E-05
55E06
55E-06
32E 05
64E 05
55E06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E-05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
51 tvg
SI avg
SI avg
SI avg
S1 avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
S1 avg
S1 avg
SI avg
St avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
St avg
SI avg
SI avg
SI avg
SI avg
Adult
Cancer
Risk
NT
NT
56E 12
74E 11
NT
NT
NT
80E-12
80E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
43E-10
53E-11
NT
NT
NT
1 3E-10
NT
1 2E-11
NT
44E-11
NT
39E-11
NT
NT
3BE-13
NT
NT
NT
NT
NT
NT
m
NT
32E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
1 4E 11
1 8E 10
NT
NT
NT
20E-1I
20E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E^»
1 3E 10
NT
NT
NT
34E-10
NT
30E-11
NT
1 1E-10
NT
97E-11
NT
NT
95E-13
NT
NT
NT
NT
NT
NT
fIT
NT
8 OF - 1 2
NT
NT
NT
NT
NT
School age
Cancer
Risk
NT
NT
84E-12
1 IE 10
NT
NT
NT
1 2E 11
1 2F-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
65E-10
79E-11
NT
NT
NT
20E-10
NT
1 8E-11
NT
66E-11
NT
58E-11
NT
NT
57E-13
NT
NT
NT
NT
NT
NT
tit
m
4 8R 12
FIT
til
(IT
m
m
Farmer
Cancer
Risk
NT
NT
1 2E 11
1 6E-10
NT
NT
NT
1 8E 11
1 8E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
96E 10
1 2E-10
NT
NT
NT
30E-10
NT
27E-11
NT
97E-11
NT
B6E-11
NT
NT
84E-13
NT
NT
NT
NT
NT
NT
NT
NT
7 IF 12
fJT
lit
NT
m
HI
                                                                                                                                              Adult      Child    School-age  Farmer
                                                                                                                                            Noncancer Noncancer  Noncancer Noncancer
                                                                                                                                               HQ        HQ        HQ       HQ
66E-07
1 3E 08
NT
2 1E-07
9 6E 08
28E^)7
1 7E-06
3 4E 07
34E-07
32E-09
NT
42E-08
NT
24E-08
84E^)7
NT
42E 07
42E-07
NT
42EX)8
60E07
42E^7
2 7E 07
31E^>4
NT
28E 10
2 1E4)8
26E^)8
47E4>7
S9E-08
1 7E-07
NT
1 1E-06
NT
77E-05
28E-05
42E45
8 4E-07
1 6E^»
NT
NT
5 IE 09
35E 08
1 7E 08
2 2E 09
84E 08
^ IF 08
NT
NT
2 IE 08
i nr 05
(IT
25E 06
50E 08
NT
80E07
36E 07
1 1E 06
63E 06
1 3E 06
1 3E 06
1 2E 08
NT
1 6E-07
NT
90E 08
32E-06
NT
1 6E 06
16E-06
NT
1 6E-07
22E06
16E06
IDE 06
1 2E 03
NT
10E09
79E 08
96E 08
1 7E 06
2 2E 07
63E07
NT
39E 06
NT
29E 04
1 OE 04
t 6E 04
32E 06
6 IE 05
NT
NT
1 9E 08
1 3F 07
6 3F 08
84F 09
3 IF 07
2 fiF 07
NT
NT
79f 08
fi 7F 05
Ml
1 5E-06
30E08
NT
4" BE -07
2 2E 07
6 3E-07
3 BE -06
7 6E-07
76E07
73EX»
NT
95E-08
NT
5 4E-08
1 9E-06
NT
95E07
9 5E-07
NT
95E08
1 3E-06
94E07
60E07
7 OE-04
NT
63E 10
4 BE 08
58E48
1 1E 06
1 3E 07
3 BE -07
NT
24E06
NT
1 7E 04
63E 05
95E 05
1 9E 06
3 7E 05
NT
NT
1 ?E 08
8 OE,08
3 BE 08
5 1F 09
1 9E 07
1 BF 07
NT
NT
48E 08
4 IF 05
til
66E-07
1 3E-08
NT
2 IE 07
9 6E 08
2 8E-07
1 7E-06
34E07
3 4E 07
32E-09
NT
4 2E-08
NT
2 4E 08
84E-07
NT
42E07
4 2E-07
NT
42E 08
60E 07
42E07
27E 07
3 IE 04
NT
2BE 10
2 IE 08
26E 08
4 7E 07
59E 08
1 7E 07
NT
1 1E-06
NT
7 7E OS
2 BE OS
42E05
84E 07
16E 05
NT
NT
5 IE 09
35E 08
1 7E 08
22E 09
84E 08
7 IF 08
NT
tit
2 IE 08
1 Be 05
til
 'oliime V. Appendix V
-------
TABLE 7  Average ln\N   -*n Risks and Noncancer HQs in Subaiea 51
CHEMICAL
Niltoanlline, 4-
NHrobenzene
Nitrophenol, 2-
Nitrophenol, 4-
N-Nttroso-di n-butylamine
N-Nitroso-di-n-piopylamlne
N-NttJosodlphenylamlne (Dlphenylamlne)
Nonachtoroblphenyl
Octachtorobrphenyl
Pentachlofobenrene
Pentachloroblphenyt
Pent»chloronttrob«nzene
P«nt»chlofoph«nol
Ph«nanthren«
Phenol
Pyt«n«
Safrole (5-(2-Pr:>penyO-1 .3 benzodioxole)
Styrene
Tetrachtorobiphenyl
Tetrachtoroethane, 1.1.1,2-
Teliachroroethane, 1,1.2.2
Tettachloroethene
Tetrachlorophenol. 2.3.4.6-
Toluene
Trichloro-1.2.2 trtfluotoethane. 1.1.2-
Trichlorobenzcne. 1.2.4-
Trlchloroblphenyl
Trtchloroethane. 1.1,1- (Methyl chloroform)
Trlchtoroethane. 1.1,2-
Trichloro«th«n«
Trtchtorotluoromettiane
Trlchlorophenol. 2,4,5-
Trichlorophenol. 2.4,6-
Vinyl acetate
Vinyl chloride
Xylene, m/p- (rrVp-CMmethyl benzene)
Xyiene. o- (o-Dimetfiyt benzene)
2.3.7.8-TCDO
.2.3.7.8PCDD
,2.3.4.7.B-HxCDO
,2.3678HxCDD
,2.3.7.8.9 HxCDO
,2,3.4,6,7,8-HpCDO
OCDD
2,3,7,8-TCDF
1, 2,3.7.8 PCDF
2.3,4.7,8-PCDF
1.2,34,7.8HxCDF
1.2,3.6,7.8-HxCDF
2.3.4.6.7.8 HxCDF
Inhalabon
Slope
Factor
(mg/kg-d)*-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
10E-02
NA
30E-01
NA
NA
15E+05
7 5E+04
1 5E+04
1 5E+04
1 5E+04
1 5E»03
1 5E»02
1 5E+04
7 5E+03
7 5E»04
1 5E»04
1 5E»04
1 5E+04
RAC
(mg/m3)
NF
00005
NF ..
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
175
1.75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
15E-01
7 5E-03
NF
7 1E-02
NA
75E-03
NA
25E03
7 5E-03
2 9E 02
2 1E*00
1 4E-02
NA
7 IE 02
1 OE-03
NA
50E-02
2 5E-02
NA
1 4E-02
NA
SOE-Ot
50E-OI
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
-------
TABLE  7  Avetago Inhalation Rr.ks and Noncancei HQs in Subaroa S 1
CHEMICAL
Nitroanlline, 4
Nifaobenzene
Nitrophenol. 2-
Hibophenol, 4
N Nrttoso-dl-n-butylamine
N Hrtroso d! n propylamme
N Nrtrosodiphenylamln* (Diphenylamme)
Nonachloioblphenyl
Octachlwobtphenyl
Pentachlorobenrene
Pentachloroblphenyl
Pentachloronrirobenzene
Pentachlorophenot
Phenanthrene
Phenol
Pyrene
Sahole (5-(2-Piopenyl)-1 .3 benzodioxole)
Slyrene
Tetrachloroblphenyl
Tetoachloroethane. 1.1.1.2-
Tebachloioethane. 1.1,2,2-
Tetrachloroethene
Tetrachlorophenol, 2.3.4.6-
Toluene
Trlchlofo-1 ,2,2-trrfluoeoethane. 1 .1 .2-
Trlchlorobenzene, 1.2.4-
Trlch'orobiph«ny!
Trlchloroethane. 1.1.1- (Methyl chloroform)
fiichloioethane. 1.1.2-
Trkrhloioethene
Trlchlorofluoiomethane
Inchlorophenol, 2.4,5-
Trichtorophenot. 2.4,6-
/Inyl acetate
/inyl chloride
f 10
                                                                                                                                             Adult      Child    School age   Farmer
                                                                                                                                           Noncancei Noncancei Noncancei Noncancet
                                                                                                                                              HQ       HQ       HQ        HO
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-06
2 BE -08
NT
1 4E-09
2 BE -08
NT
1 2E-08
NT
2 BE -08
NT
79E-07
35E-08
82E47
59E-09
1 5E-08
NT
67E-09
48E-07
NT
19E47
84E-09
NT
1 7E-07
NT
29E08
42E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
fIT
tit
NT
55E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E06
1 tE-07
NT
53E-09
1 1E-07
NT
4 5E-08
NT
1 IE-07
NT
29E-08
1 3E-07
3 IE 06
2 2E 08
55E08
NT
25E08
18E06
NT
70E-07
32E08
NT
64E07
NT
1 IE-07
16E-09
NT
NT
NT
NT
HI
fJT
NT
111
HI
fir
HI
in
in
NT
33E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E-06
63E-08
NT
32E-09
6 3E-08
NT
2 7E-08
NT
6 3E-08
NT
18E06
7 BE 08
19E 06
1 3E-08
3 3E-08
NT
15E 08
1 IE -06
NT
42E 07
19E-08
NT
39E-07
NT
66E08
95E 10
NT
NT
HT
ur
tn
NT
m
HT
HI
NT
NT
HI
HI
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
t 7E-06
2 BE 08
NT
t 4E 09
2 BE -08
NT
1 2E-08
NT
2 BE 08
NT
79E07
35E 08
82E-07
59E-09
1 5E-08
NT
67E09
4 BE -07
NT
1 9E 07
B4E 09
NT
t 7E-07
NT
29E-08
42E 10
NT
NT
NT
NT
HT
HT
m
NT
HT
NT
HI
HT
tit
 olume V. Appendix V 14
-------
TABLE 7  Average Ini.
,i Risks and Noncancet HQs in Subarea SI
CHEMICAL
1, 2.3.7.8,9 HxCDF
1.2.3 4.6.7.8 HpCDF
1.2.3,4.7.8.9-HpCDF
OCDF
Dloxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hmavatont)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NO)
Total sulfur oxides (SOx)
Participate matter
Resplrable partfcutates
Inhalation
Slope
Factor
-------
TABLE 7  Aveoge Inhalation Risks and Noncjncei HQ5 in Subaiea St
CHEMICAL
1.2.3. 7.8,9 HxCDF
1,2. 3.4.6. 7.8 HpCDF
1 2.3,4.7 8.9 HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nrbogen oxides (NOx)
Total sulfur oxides (SOx)
Particulate matter
Resplrable participates
Inhalation
Slope
Factor
(mg/kg d)«-1
1 5E + 04
1 5E«03
1 5E«03
1 5E»02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
OB4
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
OOO0263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
OOO0061
0 2625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
t OE 04
75E 05
36E 05
1 3E 03
1 3E 04
1 3E 03
25EW
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E 03
1 8E 05
75E-02
50E 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E 10
9 30E 09
1 22E 09
1 89E 08
428E-08
2 4E-04
42E 08
3 7E-05
1 5E 04
33E08
1 6E 05
7 IE 07
7 1£ 07
94E 05
43E 05
1 4E 03
50E06
4 7E^M
1 5E 05
34E 05
1 2E-04
32E 02
24E»00
9 1E-02
7 2E 02
7 2E-02
Subarea
SI avg
SI avg
SI avg
SI avg

SI avg
SI avg
S1 avg
S1 ivg
SI avg
SI avg
St avg
SI avg
S1 avg
SI avg
SI avg
SI avg
SI avg
SI avg
SI avg
S1 ivg
SI avg
St avg
St avg
SI avg
S1 avg
Adult
Cancer
Risk
2 2E 11
69E 11
90E 12
1 4E 11
69E 10
NT
NT
9 1E 09
NT
1 4E 12
4 BE 10
t 4E-10
NT
NT
NT
NT
2 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
54E 11
1 7E 10
22E 11
35E 11
1 7E 09
NT
NT
23E-08
NT
34E 12
1 2E 09
36E-10
NT
NT
NT
NT
52E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
33E 11
1 OE 10
1 4E 1 1
2 IE 11
1 OE 09
NT
NT
1 4E 08
NT
2 IE 12
72E-10
22E 10
NT
NT
NT
NT
3 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
48E 11
1 5E 10
20E 11
3 IE 11
1 5E-09
NT
NT
20E 08
NT
30E 12
1 1EO9
32E-10
NT
NT
NT
NT
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
WTES
  NA - No) applicable
  NF - Not found
  NT > No toxicrty Information
  HQ « Hazard quotient
  HI • Hazard index
                                                                               Total Risk   1 5E-08    38E-08    2 3E 08   34E-08
                                                                                                                                             Adult      Child   School-age  Farmer
                                                                                                                                           Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HQ        HQ
NT
NT
NT
NT
NT
NT
1 6E-06
1 9E 05
16E-04
IDE -09
49E06
22E4>8
1 1E-10
NT
NT
25E-03
3 BE -08
1 4E-05
46EX)7
74E-05
6 IE-OB
25E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E06
7 IE 05
60E-04
3 BE 09
18E-05
8 IE 08
41E-10
NT
NT
9 4E 03
14E-07
54E 05
1 7E 06
2 BE 04
2 3E 07
92E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36EO6
43E 05
3 6E-04
23E-09
1 IE-OS
49E08
25E-10
NT
NT
57E-03
B7E08
33E 05
1 OE 06
17EM
t 4E 07
5 5E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E06
1 9E^»
1 6E04
1 OE-O9
49E-08
22E-08
1 1E-10
NT
NT
25E4)3
3BE^»
1 4E-05
46E^)7
74E4»
6 tE^JB
25E-03
NT
NT
NT
NT
                                                                                                                                   Total HI   59E-03   2 2E 02   1 3E 02   59E-03
 olume V. Appendix V-14
-------
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TABLE 8  Average Inhalation Rrski and floncancer MQs in Subatea S2
CHEMICAL
Acenaphthene
Acenaphlhylene
Acetaldehyde
Acetone
Acetophenone
Acrylonrtrile
Anthracene
Benzene
Benzole acid
Benzotrichlotkto
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
B«nzo(g,h.l)pflrylene
B«nzo(k)fluotanthene
Bls(2-cnloroethoxy) methane
Bis(2
-------
                 /"    \
                 !      I

TABLE 8  Average ln>^_ ,,6n Risks and Noncancer HQs in Subarea S2
CHEMICAL (
Dtchlorodrfluorornelnane
Dichloroethane. 1.1- (Ethylidene dichlorlde)
Dichloroelhan*, 1 .2-
Dichloroelhene. 1.1- (VinyMdine chloride)
Dichloroethene (trans), 1 .2-
Oichlorophenol. 2.4
Dichtoropropane, 1 ,2- (Propylene dichlorlde)
Dichtoropropane (els). 1 .3
Dtchtoropropene (bans). 1 .3-
Dtethylphttialate
Dimethoxybenzldine. 3.3'-
Dtmethylphenol. 2.4-
Dtmettiytphthalale
3i-n-butytphtnalate
Dinrtrololuane. 2.6-
DlnHro-2-methylphenol, 4,6-
Dinrtrophenol. 2.4-
Onrbotoluene, 2.4
Dtoxane. t .4-
D)(n)odyl phlhalate
D. 2,4-
Ethyl melhacrylate
Ethyltonzwia
Ethylene drbromlde
Ethylene oxide
tthylene thloures
Fluoranlhen*
Fluorene
Formaldehyde
Furfural
Heptachlor
HeptachloroWphenyl
Hexachlorobenzene
Hexaentorobiphenyt
Hexachtorobutadiene
Hexachlococycrohexane. gamma (LIndane)
Haxichtorocyclopentadiene
Hexachtoroethane -;
Hexachtorophene
Hexanone, 2-
lndeno(1 ,2,3-cd)pytene
Isophorone
Maleic hydrulda
Methoxychlor
Methyl 1 butyl ether
Methyl 2-Pentanone, 4- (MIBK)
Methylene chloride
Methylnaphthalene, 2
Monochlorobiphenyl
Naphthalene
Nitroaniline. 2-
Nihoaniline. 3
Inhalation
Slope
Factor
mg/kg-d)"- 1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
78E-02
NA
NA
14E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E 03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA '
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0.175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E-02
3 BE -02
NA
2 3E 03
50E-03
75E04
29E-04
1 4E 03
1 4E-03
20E-01
NA
5 OE-03
NA
25E-02
2 5E-04
NF
50E-04
50E-04
NA
5 OE-03
2 5E 03
2 3E 02
7 1E 02
1 4E-05
NA
20E 05
1 IE 02
1 OE-02
50E 02
3 6E-03
1 3E-04
NA
2 OE 04
NA
50E05
75E-05
50E-06
2 5E-04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 1E 01
5 7E 03
2 1E-01
NF
NA
IDE 02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E-04
3E 05
3E-05
3E-05
3E^»
55E-06
3E-05
3E-05
3E-05
7E-05
2E-04
55E-06
55E-06
16E-05
55E-06
55E-06
55E-06
55E-06
49E44
5SE-06
39EO5
2 5E-04
50E-04
1 2E^)4
3 IE-OS
1 5E-10
55E^»
67E-06
81E-04
55E-06
55E-07
1 4E-08
55E06
1 4E-08
1 OE 04
55E-05
S5E-06
55E06
32E45
64E 05
55E^)6
67E-06
1 2E 04
5 5E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
S2avg
S2 avg
S2avg
S2avg
S2 avg
52 avg
S2 avg
52 avg
S2 avg
S2avg
S2 avg
S2avg
S2 avg
S2avg
S2avg
52 avg
52 avg
52 avg
52 avg
S2avg
52 avg
52 avg
S2ivg
52 avg
52 avg
52 avg
S2avg
52 avg
S2avg
52 avg
52 avg
52 avg
52 avg
S2avg
52 avg
S2avg
52 avg
52 ivg
S2avg
52 avg
52 avg
52 avg
52 avg
S2 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
Oft-site
Vapor
Cone
(ug/m3)
1 6E-05
8 3E 07
8 3E 07
8 3E-07
8 3E-07
3 6E-07
8 3E-07
8 3E-07
8 3E-07
1 1E-06
76E-06
3 6E-07
36E-07
10E-06
3 6E-07
3 6E 07
36E07
3 8E-07
33E-05
3 6E-07
2 BE -06
16E-05
33E-05
76E06
20E-08
96E-12
36E-07
4 4E-07
40E-05
36E-07
36E-08
92E 10
3 6E-07
92E-10
67E-06
36E06
36E-07
3 6E 07
2 1E-06
42E 06
36E 07
4 4E 07
76E-06
36E 08
8 3E 07
83E 07
26E 05
2 8E 06
t 1E 09
36E 0?
44E 07
44E 07
Cancer
Adult
Dose
(mg/Vg-d)
5 7E-IO
29E-11
29E 11
29E-11
29E-11
1 3E-11
29E-11
29E-11
29E-11
39E 11
2 7E-10
3E-11
3E-11
6E-11
3E-11
3E-11
3E-11
3E-11
IE 09
3E-11
90E-11
57E-10
1 2E-09
2 7E-10
71E-11
34E-16
3E-11
6E-11
4E-09
3E-11
3E 12
33E-14
1 3E-11
33E-14
23E-10
3E-10
3E-11
3E-11
4E-11
5E-10
3E 11
6E 11
2 7E 10
1 3E 12
29E 11
29E 11
92E 10
9 7E 11
39E 14
1 3E 11
1 6E 11
1 6E 11
Cancer
Child
Dose
(mg/kg-d)
1 4E-09
72E-11
72E 11
72E-11
72E-11
32E-11
72E-11
72E-11
72E-11
98E-11
6 7E-10
32E-11
32E-11
9 IE-It
32E 11
32E-11
32E-11
32E-11
29E-09
32E-11
22E-10
1 4E-09
29E-09
6 7E-10
1 BE 10
85E-16
32E-11
39E-11
35E-09
32E-11
32E-12
8 IE- 14
32E-11
81E-14
S8E-10
32E-10
32E-M
32E-11
1 9E-10
37E-10
32E 11
39E-11
6 7E-10
32E 12
72E 11
7 2E 11
2 3E 09
2 4E 10
9GE 14
32E 11
39E 11
39E 11
Cancer
School-age
Dose
(mg/kg-d)
86E-IO
44E-11
44E-11
44E-11
44E-11
1 9E-11
44E-11
44E-11
44E-11
59E-11
40E-10
1 9E-11
19E-11
55E-11
19E 11
19E-11
19E 11
19E-11
17E-09
19E-11
1 4E-10
86E-10
1 7E-09
40E-10
1 IE 10
5 IE-IB
19E-1)
23E-11
21E-09
1 9E-11
1 9E-12
49E-14
1 9E-11
49E-14
35E-10
1 9E-10
19E-11
19E-11
1 1E-10
22E-10
1 9E-11
23E 11
40E 10
1 9E 12
44E 11
44E 11
1 4E 09
1 5E 10
58E 14
1 9E 11
23E 11
2 3E 11
Cancer
Farmer
Dose
(mg/kg-d)
1 3E 09
65E 11
65E 11
65E-11
65E 11
28E-11
65E11
65E-11
65E-11
87E-11
59E-10
2 BE 11
28E-11
8 IE 11
2 BE 11
28E-11
28E-11
28E-11
2 6E 09
2BE-11
20E10
1 3E-09
26E-09
59E-10
1 6E-10
75E-16
2 BE 11
35E-11
3 1E-09
28E-11
28E-12
72E-14
2 BE 11
72E-14
52E-10
28E-10
2 BE 11
2BE-11
1 7E-10
33E-10
2 BE 11
35E-11
59E 10
28E-12
65E 11
65E-11
20E 09
22E 10
86E 14
28E II
35E It
35E 11
Noncancer
Adult
Dose
(mg/kg-d)
4 4E 09
23E 10
23E-10
23E-10
23E 10
99E-11
23E-10
23E 10
23E-10
30E-10
21E-09
99E-11
99E-11
28E 10
99E-11
99E-11
99E-11
99E-11
89E-09
99E-11
70E-10
44E-09
90E09
21E-09
55E-10
26E-15
99E 11
1 2E-10
1 1E-08
99E-11
99E-12
25E 13
99E-11
25E-13
1 BE -09
99E-10
99E ft
99E-11
5 BE 10
12E-09
99E-11
1 2E-10
2 IE 09
99E-12
23E 10
23E 10
72E 09
76E 10
30E 13
99E II
1 2E 10
1 2E 10
Moncancer
Child
Dose
(mg/kgd)
1 7E 08
84E 10
84E-10
84E-10
84E 10
37E-10
B4E-10
B4E-10
84E-10
1 1E-09
7 BE 09
37E-10
3 7E-10
1 IE 09
3 7E-10
37E-10
3 7E-10
37E-10
33E08
3 7E-10
2 BE -09
17E4W
34E-08
78E^»9
2 1E-09
99E-15
37E->0
45E-10
4 IE 08
37E-10
37E 11
95E 13
3 7E-10
95E-13
6 BE 49
37E09
37E 10
37E 10
22E 09
43E09
37E 10
45E 10
78E09
37E 11
84E 10
84E 10
2 7E 08
2 BE 09
1 1E-12
3 7E 10
45E 10
45E 10
Moncancer
School-age
Dose
(mg/kgd)
1 OE-08
51E-10
51E-10
51E-10
5 IE 10
22E-10
51E-10
5 IE 10
51E-10
69E-10
47EX»
22E-10
22E-10
64E-10
22E-10
22E-10
22E-10
22E-10
20EX)8
2 2E-10
16E09
1 OE-08
20E-OB
47E^J9
1 2E-09
80E-15
22E 10
27E 10
2 5E 08
22E 10
22E-11
57E 13
22E 10
57E 13
41E09
22E09
22E 10
22E-10
1 3E 09
26E 09
22E 10
27E 10
47E 09
22E 11
5 IE 10
5 1E 10
1 6E 08
1 7E 09
68E 13
22E 10
2 7E 10
2 7E 10
Moncancer
Farmer
Dose
(mg/kgd)
44E09
23E 10
23E-10
23E-10
23E 10
99E 11
23E-10
23E-10
2 3E 10
30E-10
2 1E-09
99E-11
99E-11
28E-10
99E 11
99E 11
99E-11
99E-11
B9E-09
99E 11
70E-10
44E09
90E09
2IE09
55E-10
26E 15
99E 11
1 2E 10
1 IE 08
99E-11
99E-12
25E 13
99E-11
25E 13
18E09
99E-10
99E-M
99E 11
58E-10
12E09
99E 11
1 2E 10
2 IE 09
99E 12
23E 10
23E 10
72E 09
76E 10
30E 13
99E 11
1 2E 10
1 2E 10
Volume V. Appendrx V-14
-------
TABLE 8  Avetage Inhalation Risks and fjoncance' HQs tn r>ubarra S?
CHEMICAL
Dtchlotodifluoromethane
Dichloroelhane. 11 (Ethylidene dichlonde)
Dichloroelhane. 1.2
Dichloroeth«n«. 1.1- (Vinylidine chloride)
Dichloroothene (trans). 1.2-
Dlchlorophenol. 2.4-
Dichloropropane. 1 .2- (Ptopylene dichloride)
Dichloropropene (cis). 1.3-
Dichloropropen* (dans). 1,3-
Diettiylphthalate
Dlm»thoxyb0ruidinc, 3.3'-
Dlmettiylphenol. 2.4-
Dimelhylphlhalale
Di n-butylphthalale
Dlnitiotoluene. 26
Dinlbo-Z-mettiylphenol. 4.6-
Dmltrophenol, 2.4-
Dinrtrololuene. 2.4-
Dioane, 1.4-
Di(n)octy) phthalate
D.2.4
Ethyl methacrylate
Ethylb«ruene
Ethylen* dibtom-.de
Ethylene oxide
Etfiylene Kiiouiea
Fluoranthene
Fluoi«n»
Formaldehyde
Furfural
Heptachlol
Heptachlorobiphenyl
Hexachlorobenzene
Hexachloroblphenyl
Hexachlorobutadiene
Hexachloiocycloh«xan«, gamma (Lindane)
Hexachlorocyclopentadierie
Hexachloroethane
Hexachlorophene x:
Hexanona, 2-
lndeno(1 ,2.3-<:d)pyrene
Isophorone
Malelc hydiazide
Methoxychlor
Methyl 1 butyl elher
Methyl-2-Pentanone. 4 (MI8K)
Methylene chloride
Mettiylnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nitroaniline 2-
Nitroanilme 3
Inhalahon
Slope
Factor
(mg/kg d)"-1
NA
NA
9 IE 02
1 2E»00
NA
NA
NA
1 3E4>1
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
7 8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E 03
NF
NA
NA
N'A
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
o ooon^
NF
Inhalation
RfD
(mg/kg-d)
1 4E-02
36E-02
NA
23E 03
50E 03
7 5E 04
29E 04
1 4E 03
1 4E 03
20E-01
NA
50E-03
NA
2 5E 02
2 5E 04
NF
50E 04
50E-04
NA
50E 03
25E 03
23E 02
7 IE 02
1 4£ 05
NA
20E 05
1 OE 02
1 OE 02
50E 02
36E 03
1 3E-04
NA
2 OE-04
NA
50E05
7 5E 05
50E 06
25E 04
7 5E 05
NF
NA
50E 02
1 3E Ot
1 3E 03
2 IE 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E 05
tlf
Emission
Rale
(g/sec)
25E04
1 3E 05
1 3E 05
1 3E 05
1 3EO5
55E-06
1 3E 05
1 3E 05
1 3E^K
1 7E-05
1 2E-04
55E-08
55E-06
1 BE -05
55E-06
55E-08
55E-06
55E 06
49E^)4
55E06
39E05
25E04
50E04
t 2FX>4
3 IE OS
1 5E 10
55E-06
67E4J6
61EX)4
55E06
55E 07
1 4E 08
55E06
1 4E 08
1 OEO4
5 5E 05
55E06
55E06
32E05
64E05
55E 06
6 7E 06
1 2E 04
5 5E 07
1 3E 05
1 3E 05
40E 04
4 2E 05
1 7E 08
55E 06
6 7E OC
6 7E 06
Subarea
52 avg
S2 avg
S2avg
S2 avg
S2 avg
S2avg
S2avg
S2 ivg
S2 ivg
S2 avg
S2avg
52 avg
52 avg
52 ivg
52 avg
S2avg
52 avg
S2 avg
S2avg
S2 avg
S2avg
S2 avg
S2avg
S2ivg
S2avg
S2avg
S2 avg
S2 avg
52 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
S2avg
S2 avg
S2 avg
S2 avg
S2avg
S2 avg
52 avg
S2 avg
S2 avg
52 avg
52 avg
S2 avg
S2 avg
52 avg
S2 avg
52 avg
S2 avg
S2 a,q
AduH
Cancer
Risk
NT
NT
26E-12
3 5E 1 1
NT
NT
NT
38E-12
38E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E-10
25E-11
NT
NT
NT
63E 11
NT
5 BE 12
NT
2 1E-11
NT
1 8E 11
NT
NT
1 8E-13
NT
NT
NT
NT
OT
NT
NT
NT
1 5E 12
NT
NT
Nt
IIT
NT
Child
Cancer
Risk
NT
NT
66E-12
87E It
NT
NT
NT
94E 12
94E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
51E 10
62E 11
NT
NT
NT
1 6E 10
NT
1 4E-11
NT
5 1E-11
NT
46E-11
NT
NT
45E-13
NT
NT
NT
NT
NT
NT
NT
NT
38E 12
fIT
NT
HI
in
NT
School age
Cancer
Risk
NT
NT
40E 12
52E 11
NT
NT
NT
57E 12
57F. 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
31E 10
37E-11
NT
NT
NT
96E-11
NT
87E-12
NT
3 IE 11
NT
28E-11
NT
NT
2 7E 13
NT
NT
NT
NT
in
NT
m
NT
2 3F. 12
NT
NT
NT
III
NT
Farmer
Cancer
Risk
NT
NT
59E 12
7 7E-11
NT
NT
NT
84E 12
84E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
45E 10
55E-11
NT
NT
NT
1 4E 10
NT
13E-11
NT
46E 11
NT
4 1E-11
NT
NT
40E-13
NT
NT
NT
NT
in
NT
NT
NT
3 4K 12
Nt
NT
NT
III
NT
                                                                                                                                                Adult      Child   School age   Farmer
                                                                                                                                              Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                 HQ       HQ       HQ        HQ
31E 07
63E 09
NT
1 OE-07
45E08
1 3E 07
79E 07
1 6E 07
1 6E 07
1 5E-09
NT
2 OE 08
NT
1 IE 08
4 OE 07
NT
2 OE 07
2 OE 07
NT
2 OE-08
28E-07
2 OE-07
1 3E 07
1 5E-04
NT
1 3E-10
99E09
1 2E 08
2 2E 07
28E-08
8 OE-08
NT
5 OE-07
NT
37E 05
1 3E 05
20E05
40E 07
7 7E-06
NT
NT
24E 09
1 7E 08
80E 09
1 IE 09
40E 08
3 IF. 08
NT
NT
99E 09
BSF 06
rn
1 2E 06
24E 08
NT
38E 07
1 7E 07
50E 07
30E 06
59E 07
59E07
5 7E-09
NT
7 4E 08
NT
42E 08
15E 06
NT
74E 07
74E 07
NT
74E 08
1 OE 06
74E07
4 7E 07
54E04
NT
49E 10
37E 08
45E 08
82E 07
10E 07
30E 07
NT
1 9E 06
NT
t 4E 04
49E 05
74E 05
1 5E 06
29E 05
NT
NT
90E 09
62E 08
30E 08
39F 09
1 r;f 07
1 ?t 07
NT
IH
3 7f 08
3 ?f l)r>
Ml
7 OE 07
1 4E 08
NT
2 3E 07
1 OE 07
30E 07
18E 06
36E 07
36E-07
34E-09
NT
45E-08
NT
26E-08
9 OE-07
NT
45E-07
45E^)7
NT
45EX>6
63E-07
44E4)7
2 BE 07
33E04
NT
30E 10
22E 08
27E08
50E 07
63E 08
1 BE 07
NT
1 IE 06
NT
82E 05
30E 05
4 5E 05
90E 07
1 7E 05
NT
NT
55E 09
3 BE, 08
1 BE 08
24E 09
89F 08
7 r.F 08
NT
Nt
2 ?E 08
1 Of 05
NT
31E 07
6 3E 09
NT
1 OE 07
45E08
1 3E 07
79E 07
1 6E 07
t 6E 07
1 5E 09
NT
20E 08
NT
1 1E 08
4 OE-07
NT
2 OE 07
2 OE-07
NT
20EX)8
2 BE 07
20E07
1 3E07
1 5E 04
NT
1 3E 10
99E 09
1 2E 08
22E 07
2 BE 08
BOE 08
NT
50E 07
NT
37E 05
t 3E 05
20E 05
40E 07
7 7E 06
NT
NT
24E 09
1 7E 08
80E 09
1 IE 09
40E 08
3 IF 08
NT
NT
99E 09
8 SF. 06
NT
/olume V Append" V 14
-------
TABLE 8  Average Inhalation Risks and Noncancee HQs in Subarea S2
CHEMICAL
Nrtroanfline, 4-
Nitrobenzene
Nltrophenol. 2-
Nldopheno). 4-
N-Nilroso-di-n-butylamin»
N-Nttroso-dl-n-propylamlna
N-Nrtrosodiphenytemtne (Diphenylamine)
Nonachlorobiphenyl
OcUchloroblphenyl
Pentachlorobenzene
Pentachloroblphenyl
Pentachloronrtrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl)- 1 ,3-benzodloxole)
Styrene
TetTachloroblphenyl
Tetrachloroethane, 1.1.1,2
Tetrachloroethane. 1.1.2.2-
Tetrachloroethene
Tetrachlorophenol, 2,3,4.8-
Toluene
Trichloro-1,2.2-trffluoroethane, 1.1.2-
Trkhlorobenzene. 1,2.4-
Trkhlofoblphenyl
Trlchlofoethane, 1,1,1- (Methyl chloroloim)
TrIchlofMttiin*. 1,1,2-
Trlchloroethene
Trkhlorofluoromethane
Trtchlorophenol, 2.4,5-
TrichkHOphenol. 2.4,6-
Vlnyl acetate
Vinyl chloride
Xylene. m/p- (m/p-Dimethyl benzene)
Xylene, o- (o-Dimethyt benzene)
2.3.7.8TCDD
1. 2.3.7,8 PCDD
1. 2.3,4, 7,8-HxCDO
1.2.3.6,7.8-HxCDD
1.2.3.7.8.9 HxCDD
1.2.3.4.6.7.8-HpCDD
OCOD
2.3.7.8-TCDF
1.2,3.7.8-PCDF
2.3,4.7.8 PCDF
12347 8 HxCDF
1,2.3.6.7 ,8 HxCDF
2.3.46.7,8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)M
NF
NA
NF
NF
">4E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
606-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
15E+05
7 5E+04
1 5E+04
5E+04
5E+04
5E»03
5E«02
5E«04
5E«03-
5E»04
5E+04
5E«04
5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA-
NA
NA
NA
NA
NA
7 5E-04
75E-03
NA
1 5E-01
75E-03
NF
71E-02
NA
75E-03
NA
25E43
75E4)3
29E-02
2 1E»00
1 4E-02
NA
7 1E-02
1 OE^M
NA
5 OE-02
2 5E-02
NA
14E-02
NA
5 OE 01
50E 01
NA
NA
NA
NA
NA
NA
HA
NA
HA
HA
HA
HA
HA
Emission
Rate
(g/sec)
87E-06
55E-06
87E-08
55E06
1 2E-04
67E-06
67E-06
1 4E-08
1 4E-06
4 BE -05
1 4E 08
34E-05
55E-06
67E-06
55E-06
55E-06
1 2E 04
23E-05
1 4E-08
55E06
55E06
5 IE-OS
6 BE 06
6 IE 04
33E-04
55E06
30E08
1 3E-05
1 3E-05
1 9E-05
2 5E-04
55E-06
55E-06
64E-05
2 5E 04
3 BE 04
55E-06
1 08E 11
6 7BE 11
895E II
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
S2avg
S2 avg
S2avg
52 avg
S2avg
S2 avg
52 avg
S2 avg
S2avg
52 avg
S2avg
S2avg
S2avg
S2avg
S2avg
52 avg
S2avg
52 avg
S2avg
S2 avg
S2 avg
S2avg
S2 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
52 avg
S2 avg
S2 avg
52 avg
S2 avg
52 avg
52 avg
52 avg
52 avg
52 avg
S? avg
Ofl-site
Vapor
Cone
(ug/m3)
44E07
36E 07
4 4E 07
3 6E-07
80E 06
4 4E 07
4 4E-07
92E-10
92E-10
31E-06
92E-10
22E-08
366-07
4 4E-07
3 6E 07
36E-07
76E06
1 5E-06
92E-10
36E^)7
3 6E 07
34E-06
45E07
40E-05
22E-P5
36E-07
20EXI9
8 3E-07
8 3E 07
1 2E-06
1 6E-OS
3 6E-07
3 6E-07
42E-06
1 6E-05
2 5E-05
3 6E-07
7 IE 13
45E 12
59E 12
1 IE 11
72E 12
82E 11
* IE 10
58E 12
2 3E II
3 1E 11
94E II
8 BE 11
99E II
Cancer
Adult
Dose
(mg/kg-d)
16E 11
1 3E-11
16E It
1 3E 11
28E-10
16E-11
16E-11
33E-14
33E-14
1 1E-10
33E-14
78E-11
13E-11
1 6E-11
1 3E-11
1 3E-11
27E-10
52E-11
33E-14
3E 11
3E-11
2E-10
6E-11
4E-09
7 7E-10
1 3E-11
70E-14
29E-11
29E11
43E-11
57E-10
1 3E-11
1 3E-11
1 5E-10
57E-10
88E-10
1 3E 11
25E 17
1 6E 16
2 IE 16
3 BE 16
25E 16
29E 15
t 4E 14
20E 16
80E 16
1 IE 15
3 3E 15
3 1C 15
35E 15
Cancer
Child
Dose
(mgrtig-d)
39E 11
32E 11
39E 11
32E 11
70E-10
39E 11
39E 11
81E-14
8 IE 14
28E-10
B1E-14
20E-10
32E-11
39E-11
32E 11
32E-11
67E-10
1 3E-10
8 IE 14
32E-11
32E-11
30E-10
39E-11
35E-09
19E-09
32E-11
1 7E-13
72E-1I
72E-11
1 IE 10
1 4E-09
32E-11
32E-11
37E-10
14E09
22E09
32E-11
63E 17
39E 16
52E 16
96E 16
63E 16
7 2E 15
36E 14
5 IE 16
20E 15
2 7E 15
83E 15
7 7F 15
8 7E 15
Cancer
School-age
Dose
(mg/fcg-d)
23E-II
1 9E-11
23E-II
1 9E-11
4.2E-10
23E-11
23E-I1
49E-14
49E-14
1 7E-10
49E-14
1 2E-10
1 9E-11
23E-11
1 9E-11
19E-11
4 OE-10
79E-11
49E-14
19E 11
19E-11
1 BE 10
24E-11
2 1E-09
1 2E-09
19E-11
1 IE 13
44E-11
44E-11
65E-11
86E-10
19E-11
19E-11
2 2E-10
86E-10
1 3E-09
1 9E-11
38E 17
24E 16
3 IE 16
58E 16
38E 16
43E 15
22E 14
3 IE 16
1 2E 15
1 6E 15
50E 15
4 7E 15
53E 15
Cancer
Farmer
Dose
(mg/kg-d)
35E 11
28E-11
35E-1I
28E-11
62E-10
35E-11
35E-11
72E-14
72E-14
25E-10
72E-14
1 7E-10
2 BE 11
35E-11
28E-11
2 BE 11
59E-10
1 2E-10
72E-14
28E-11
28E-11
26E-10
35E-11
32E-09
1 7E-09
28E-11
16E-13
65E-11
65E-11
96E-11
1 3E-09
28E-11
28E-11
33E-10
13E-09
20E-09
28E-11
56E-17
35E-16
46E 16
86E 16
56E 16
64E 15
32E 14
45E 16
1 BE 15
24E 15
74E 15
69F 15
?ar 15
Noncancei
Adult
Dose
(mg/kg-d)
1 2E 10
99E-11
1 2E-10
99E-11
22E-09
1 2E-10
1 2E-10
25E 13
25E-13
86E-10
25E-13
6 IE 10
99E-11
1 2E-10
99E-11
99E-11
21E-09
41E-10
25E-13
99E-11
99E 11
93E-10
1 2E-10
1 1E-OB
60E-09
99E-11
55E-13
23E-10
23E-10
34E-10
4 4E 09
99E-11
99E-11
1 2E-09
44E-09
69E-09
99E-11
20E 16
1 2E 15
1 6E 15
30E 15
20E 15
22E 14
1 IE 13
1 6E 15
62E 15
84E 15
26E 14
2 4E 14
? ?r. 14
'•loncancer
Child
Dose
(mg/kg-d)
45E-10
37E-10
45E-10
37E-10
82E-09
45E-10
45E-10
95E-13
95E 13
32E09
95E-13
23E-09
37E-10
45E-10
37E-10
3 7E-10
78E-09
15E49
95E-13
3 7E-10
37E-10
35E-09
46E-10
4 IE-OS
2 2E 08
3 7E-10
20E-12 '
84E 10
84E-10
1 3E-09
1 7E-OB
3 7E-10
3 7E-10
43E-09
1 7E-08
2 6E-08
37E-10
73E 16
46E 15
60E 15
1 IE 14
74E 15
B 4E 14
4 2E 13
59E 15
2 3E 14
32E 14
9GF 14
90E 14
1 OC 13
loncancer
School-age
Dose
(mg/kg^J)
27E-10
22E-10
27E tO
22E-10
49E-09
27E-10
2 7E-10
57E-13
57E-13
19E-09
57E-13
1 4E-09
22E-10
2 7E-10
22E-10
22E-10
47E-09
92E-10
57E-13
22E-10
22E 10
21E-09
28E 10
2 SE 08
1 3E-08
22E 10
1 2E-12
5 IE 10
5 IE 10
76E-10
1 OE 08
22E 10
22E 10
26E09
1 OE 08
1 6E 08
22E-10
44E 16
2 BE 15
37E 15
6 BE 15
44E 15
- 5 IE 14
25E 13
36E 15
1 4E 14
1 9E 14
5 BE 14
54E 14
6 IE 14
loncancer
Farmer
Dose
(mg/kg-d)
1 2E-IO
99E-11
1 2E-10
99E 11
22E-09
12E-10
12E-10
25E 13
25E-13
B6E-10
25E-13
61E-10
99E 11
12E-10
99E 11
99E-11
2 1E-09
41E-10
25E-13
99E-11
99E 11
93E-10
12E 10
1 1E 08
60E-09
99E 11
55E13
2 3E-10
2 3E 10
34E 10
44E-09
99E 11
99E-11
12E09
44E09
69E-09
99E-11
20E 16
1 2E 15
16E 15
30E 15
20E 15
22E 14
I IE 13
1 6E 15
62E 15
84E 15
26E 14
24E 14
? 7E 14
Volume V. Appendix V-14
-------
TABt F 8  Average Inhalation Risks arid f-loncancei HOs in Subaroa S?
CHEMICAL
Nitroaniline, 4-
Nittobenrene
Nitrophenol. 2-
Nitiophenol. 4
N Nitroso-di-n-butylamlne
N Nitfoso-di-n-piopytamine
N Nitrosodiphenylamln* (Diphenylamine)
Nonachlorobiphenyl
Octachloroblphany)
Pentachloiobenzene
Pentachlorobiphenyl
Pentachloronrtrobenzene
Pentachlofophenol
Phenanthrena
Phenol
Pyrene
Safrola (5-(2-Propenyl)-1 .3 benzodioxole)
Styiene
Tetrachtofoblphenyl
Tebachloroethane. 1.1.1 2
Tetoachloioethane. 1.1.2.2-
Tetrachtofoethene
Tetrachlorophenol, 2.3.4.6-
Toluene
Trlchloto-1.2,2 tiifluoioethane. 1.1 2
Trichtorobenzene. 1.2,4
TrichKjroblphenyl
TrtchkHoethane, 1,1.1- (Methyl chloroform)
Trichkxoethan*. 1.1.2-
Trichtoroethene
Tr*chk>rofluoromethane
Trfchlofophenol, 2.4.5-
Trichlotophenol, 2,4.6-
Vinyl acetate
/myl chloride
Xytene. m/p- (m/p-Dimethyl benzene)
Kylene. o- (o-Dimethyl benzene)
J.3.7.8-TCDD
1 2.3.7.8PCDO
1 2.3.4 7,8-HxCDD
1 2.3 6 7.8-HxCDD
12378 9 HxCDD
1.2.3.4 6. 7.6 HpC DO
DC DO
'.3 78 TCDF
12378 PCDF
' 3. 4 7. 8 PCDF
12347 8 HxCDF
123678 H«CDF
'34678 H
-------
TABLE 8  Average li
                Ink..
o'n Risks and Noncancei HQs in Subaiea S2
CHEMICAL
1.2.3.7.8.9-HxCDF
1.2.3467.8HpCDF
1.2.3.4,7,8.9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (haxavilant)
Chromium (frivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Respirable particulates
Inhalation
Slope
Factor
(mg/kg-d)M
1 5E+04
1 5E»03
1 5E+03
1 5E+02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0 004375
0875
NA
NA
0000075
00175
0 004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/Vg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E05
1 3E-03
1 3E-04
1 3E-03
25E-01
NA
NA
2 IE OS
5 OE-03
1 3E 03
1 3E-03
1 BE -05
75E-02
S0?44
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E 09
1 B9E 08
4 28E-08
.24E44
42E-06
37E-05
15E-04
33E-08
1 6E-05
7 1E-07
7 1E-07
94E^)5
43E^»
1 4E-03
50E06
47E-04
1 5E-05
34E-05
1 2E-04
32E-02
24E+00
9 1E-02
72E-02
72E-02
Subarea
S2 avg
S2avg
52 avg
S2 avg

S2 avg
S2avg
S2 avg
S2avg
S2 avg
S2avg
S2avg
S2 avg
S2avg
52 avg
S2 avg
S2avg
S2avg
S2avg
S2 avg
S2avg
52 avg
S2 avg
S2 avg
S2 avg
S2avg
Offsite
Vapor
Cone
(ug/m3>
1 9E 11
6 IE 10
8 1E-11
1 3E-09
2 BE -09
16E-05
2 BE -07
24E-08
89E-06
22E-09
1 1E^)6
47E-08
47E-08
82E-06
2 BE -08
92E-05
33E-07
3 IE-OS
9 9E-07
22E-06
79E-06
2 tE4)3
1 6E-01
6 OE-03
4 BE -03
4 BE -03
Cancer
Adult
Dose
(mg/kg-d)
6 BE 16
22E-14
2 BE 15
44E-14
99E-14
56E 10
9 BE 12
86E-11
35E-10
77E-14
37E-11
1 6E-12
16E 12
22E 10
1 OE 10
33E-09
12E-11
1 1E-09
35E-11
79E-11
28E-10
7 4E-08
56E-06
2 1E-07
1 7E-07
1 7E-07
Cancer
Child
Dose
(mg/kg-d)
1 7E-15
54E 14
7 IE 15
1 1E-13
25E-13
1 4E-09
24E-11
21E 10
B7E-10
1 9E-13
93E-11
41E-12
41E-12
54E-10
25E-10
8 1E-09
29E-11
27E-09
87E-11
20E-10
69E-10
19E-07
1 4E-05
5 3E-07
4 2E-07
4 2E-07
Cancer
School-age
Dose
(mg/kg-d)
10E-15
33E 14
43E-15
66E-14
15E-13
84E-10
1 5E-11
1 3E-10
52E-10
12E-13
S6E-11
25E-12
25E-12
33E-10
1 5E-10
49E-09
1 7E-11
1 6E-09
52E-11
1 2E-10
42E-10
t 1E-07
8SE-06
3 2E-07
2 5E-07
2 5E-07
Cancer
Farmer
Dose
(mg/kg-d)
1 5E-15
48E-14
63E 15
9BE-14
22E-13
1 2E-09
22E 11
1 9E-10
7 7E-10
1 7E-13
83E-11
37E-12
37E-12
49E-10
22E-10
72E-09
26E-11
24E-09
77E-11
1 BE-10
62E-10
1 7E-07
12E4W
4 7E-07
3 7E-07
37E-07
Noncancer
Adult
Dose
(mg/kg-d)
53E-15
1 7E-13
22E-14
34E-13
77E-13
43E-09
76E-11
67E-10
27E-09
60E-13
29E-10
1 3E-11
13E-11
1 7E-09
78E-10
2 5E-08
90E-11
BSE 4)9
2 7E-10
6 IE 10
22E-09
58E07
44E-05
16E-06
13E-08
1 3E-06
Noncancer
Child
Dose
(mg/kgd)
20E-14
63E-13
82E-14
1 3E-12
29E-12
1 6E-08
2 BE-10
25E-09
10E-08
22E-12
1 1E-09
48E-11
48E-11
63E09
29E-09
95E-08
34E-10
32E^»
10E-09
23E^»
81E-09
22E^W
1 6E-04
61E46
49E-08
49E-06
Noncancei
School-age
Dose
(mg/kg-d)
1 2E-14
3 BE 13
50E-14
77E-13
1 7E-12
98E-09
1 7E-10
15E-09
61E-09
1 3E-12
65E-10
29E-11
29E-11
3 BE 09
18E09
5 7E-08
20E 10
1 9E-08
61E-10
14E09
49E-09
13E06
99E-05
37E06
29E06
29E06
Noncancer
Farmei
Dose
(mg/kg-d)
53E-15
1 7E-13
22E-14
34E-13
77E-13
43E-09
76E-11
67E-10
27E09
60E-13
29E-10
13E-11
13E-11
1 7E-09
7 BE 10
2 5E-08
90E-11
85E-09
27E 10
6 IE 10
22E-09
5 BE -07
44E-05
16E-06
1 3E-06
13E-06
NOTES:
  NA - Not applicable
  NF - Not found      *:
  NT • No toxicity Information
  HQ * Hazard quotient
  HI -Hazard Index
/olume V. Appendix V-14
-------
TABLE 8  Average Inhalation Risks and f Joncancef HQs in Subarea S2
CHEMICAL
1.2 37.89 HxCDF
t.2.34.6.78 HpCDF
1 2.3.4.7.8.9 HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (divalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
-lydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
'articulate matter
3espirable particulates
Inhalation
Slope
Factor
(mg/kg d)"-1
1 5E«04
1 5E»03
1 5E+03
1 5E*02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E 05
36E-05
1 3E 03
1 3E 04
1 3E-03
25E-01
NA
NA
2 1E 05
5 OE 03
1 3E 03
1 3E 03
1 8E-05
75E 02
5 OE-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E 09
1 22E 09
1 89E 08
4 28E-08
24E04
42E06
37E4«
1 5E^4
33E^>8
16EXS
7 1E^)7
7 1E 07
94E05
43E«
1 4E4)3
50E^»
4 7E-04
15E-05
34E^»
1 2E-04
32E-02
24E*00
9 IE -02
72E^)2
72E02
Subaiea
S2 avg
S2 avg
S2 avg
S2 avg

S2 avg
S2 avg
S2 avg
S2 avg
S2 ivg
52 avg
SI' avg
S2avg
S2 avg
S2 avg
S2 avg
S2 avg
S2avg
S2 avg
S2 avg
S2 ivg
S2 avg
S2 avg
S2 avg
S2 avg
S2 avg
Adult
Cancer
Risk
1 OE 11
32E 11
43E 12
66E-12
33E-10
NT
NT
43E-O9
NT
64E-13
2 3E-10
68E-11
NT
NT
NT
NT
98E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
25E 11
8 1E-11
1 IE 11
1 6E 11
82E 10
NT
NT
1 IE-OS
NT
1 6E-12
57E 10
1 7E-10
NT
NT
NT
NT
24E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
1 5E 11
49E 11
64E 12
99E 12
49E 10
NT
NT
65E-09
NT
97E-13
34E-10
1 OE-10
NT
NT
NT
NT
1 5E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
2 3E 11
72E 11
95E 12
1 5E-11
73E 10
NT
NT
96E 09
NT
1 4E 12
5 OE-10
1 5E-10
NT
NT
NT
NT
22E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
^JOTES
  NA - Not applicable
  NF « Not found
  NT = No toxicity information
  HO « Hazard quotient
  HI = Hazard index
                                                                                Total Risk    73E-09    1 8E-08    1 IE-OS    t 6E-08
                                                                                                                                                Adult      Child    School-age   Farmer
                                                                                                                                              Noncancer  Noncancer  Noncancer Noncancer
                                                                                                                                                 HQ        HQ        HQ       HQ
NT
NT
NT
NT
NT
NT
76E 07
89E-06
7 6E-05
4BE-10
23E-06
1 OE-08
51E-11
NT
NT
1 2E-03
1 BE 08
68E-06
2 2E-07
3 5E 05
2 9E-08
1 2E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E 06
33E 05
28E04
1 8E 09
86E 06
3 BE 08
1 9E-10
NT
NT
44E03
6 BE 08
25E 05
8 IE 07
1 3E 04
1 1E-07
4 3E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 06
20E 05
1 7E4)4
1 IE 09
52E-06
23E 08
1 2E-10
NT
NT
2 7E 03
4 IE 08
1 5E 05
4 9E 07
7 9E 05
65E 08
2 6E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
76E 07
89E06
7 6E 05
4 BE 10
23E06
1 OE 08
5 IE-It
NT
NT
1 2E 03
1 8E 08
68E06
22E07
3 5E 05
29E 08
1 2E 03
NT
NT
NT
NT
                                                                                                                                     Total HI   28E-03   1 OE 02   6 3E 03    2 BE 03
 'olume V, Append!" V-
-------
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-------
TABLE 9  Average Inhalation Ri^ks and Noncancer HQs in Subaica S3
CHEMICAL
Acenaphthene
Acenaphthylena
Acetaldehyde
Acetone
Acelophenone
Acrylonitrile
Anthracene
Benzene
Benzole acid
Benzobichloride
Benzo(a)anthrac«ne
Beruro(a)pyrene
Beruo(b)fluofanthena
Benzo(g ,h ,i)perylene
Bento(k)fluoranthene
Bls(2-chloroelhoxy) methane
Bis(2 -chk>roethyl)ether
Bls(2-chlorolsopropyl)ether
3ls(2-elhyihexyl)phthaiate
Bromodrchloromethane
Bromoform
3romomethane
jromodiphenyl ether, p
3utanone. 2- (Methyl ethyl ketone)
Butylbei irylphmalale
Carbon disulfide
Zarb^n tetracblorHe
^hlofdane
'hloto-3-msthylphenol, 4-
;hk>foanillne. p- (4-Chloroaniline)
Dhloroberurene
;i,iotobenrilate
:hloroethane (Ethyl chloride)
Chloroform
;tiloiomethane
;hloronaphthalene, beta
:hlorophenol. 2-
:hloiodiph«nyl ethei. 4-
Ihrysene *;
:tesol, m-
Diesel, o- (2-Methylphenol)
^resol, p-
xrotonaldehyde
",umene
)DE.4,4'-
)ibenz(a.h)anthracene
)ibromochloromethane
)ichlorobenzene, 1 .3-
)ichlorobeniene, 1.4-
lichloiobenrene, 1.2-
)ichlorobenridine, 3 3'-
)ichlofobiphenyl
Inhalation
Slope
Factor
(mg/kg.d)*-1
NA
NF
7 7E 03
NA
NA
2 4E 01
NA
29E 02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E 03
NA
NA
NA
NA
NA
53E 02
1 3E»00
NF
NA
NA
2 7E-01
NA
8 1E-02
6 3E 03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
OOOO053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
HA
NA
Inhalation
RID
(nig/kg d)
1 5E-02
NF
6 IE 04
25E 02
25E02
1 4E 04
75E02
43E04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE-02
50E-03
5 OE 03
50E 03
36E 04
NA
7 1E 02
50E 02
1E 04
4E 04
5E-05
NF
OE 03
4E 03
50E03
7 1E-01
25E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
64E 04
NA
NA
50E 03
NA
5 7E 02
1 4E 02
(IA
NA
Emission
Rate
(g/sec)
67E06
67E06
30E 04
29E03
29E 04
2 OE 04
55E06
1 5E 05
1 IE 05
32E05
55E06
55E06
55E06
55E 06
55E-06
67E 06
1 3E 05
67E-06
37E-05
1 OE 04
55E 06
4 9E 04
6 7E 06
5 1E 05
55E 06
89E 05
1 6E 04
55E 07
67E 06
67E 06
55E 06
37E 05
49E 04
27E 04
25E 04
67E 06
55E 06
67E 06
55E 06
55E06
55E 06
55E 06
1 4E 04
55E 06
55E07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
S3 avg
S3 avg
S3 avg
S3 avg
S3 ivg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3*vg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
53 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
Adult
Cancer
Risk
NT
NT
2 4E 12
NT
NT
49E 11
NT
44E 13
NT
NT
NT
NT
NT
NT
NT
NT
1 5E-H
NT
NT
NT
22E 14
NT
NT
NT
NT
NT
85E 12
73E-13
NT
NT
NT
1 OE-11
NT
22E 11
16E-12
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
m
m
fir
tIT
m
NT
Child
Cancer
Risk
NT
NT
59E-12
NT
NT
1 2E 10
NT
1 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
3 7E-11
NT
NT
NT
54E-14
NT
NT
NT
NT
NT
2 IE 11
1 BE 12
NT
NT
NT
26E tl
NT
54E 11
39E-12
NT
NT
NT
NT
NT
NT
NT
NT
m
nr
nr
IIT
tir
m
tn
m
NJ
School age
Cancer
Risk
NT
NT
36E-12
NT
NT
74E-11
NT
66E 13
NT
NT
NT
NT
NT
NT
NT
NT
22E-11
NT
NT
NT
33E-14
NT
NT
NT
NT
NT
1 3E 11
1 1E-12
NT
NT
NT
1 5E-11
NT
33E-11
24E-12
NT
NT
NT
NT
NT
NT
NT
NT
IIT
nr
NT
III
in
til
til
m
m
Farmer
Cancer
Risk
NT
NT
53E 12
NT
NT
1 1E-10
NT
97E-13
NT
NT
NT
NT
NT
NT
NT
NT
33E 11
NT
NT
NT
4 BE 14
NT
NT
NT
NT
NT
1 9E 11
1 6E-12
NT
NT
NT
23E-11
NT
49E 11
35E-12
NT
NT
NT
NT
NT
NT
NT
NT
HT
NT
nr
tir
ur
in
m
m
m
                                                                                                                                             Adult      Child   School age   Farmer
                                                                                                                                          Noncancer Noncancer Noncancer Noncancer
                                                                                                                                             HO       HQ       HO       HQ
35E-09
NT
37E 06
92E 07
9 3E 08
1 1E 05
5 BE 10
2 7E 07
9 OE-11
NT
NT
NT
NT
NT
NT
NT
NT
53E-09
5 9E-08
1 6E-07
87E 09
1 IE-OS
NT
57E09
87E 10
9 9E 07
BSE -06
2 9E-07
NT
53E 08
3 IE 08
58E-08
54E4W
BSE -07
NT
27E09
35E-08
Nl
NT
35E 09
35E09
3 5E 08
NT
68E 08
NT
Nr
4 ?E 08
ur
7 RE 10
1 IF 09
nr
nr
1 3E 08
NT
1 4E 05
34E 06
35E07
42E 05
22E 09
10E06
34E-10
NT
NT
NT
NT
NT
NT
NT
NT
20E 08
22E07
6 IE 07
33E 08
4 IE 05
NT
2 IE 08
33E09
37E06
33E 05
1 1E 06
NT
20E 07
1 IE 07
2 2E 07
20E 08
32E 06
NT
99E 09
1 3E 07
NT
NT
1 3E 08
1 3E 08
1 3E 07
NT
25F 07
NT
NF
1 r,r 07
rn
2 f)E 09
1 IT 08
nr
rn
BOE 09
NT
84E 06
2 IE 06
2 IE 07
25E 05
1 3E 09
62E 07
20E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-08
1 3E 07
3 7E 07
2 OE 08
2 5E-05
NT
1 3E 08
20E 09
22E 06
20E 05
66E 07
NT
1 2E 07
69E 08
1 3E 07
1 2E 08
1 9E 06
NT
60E 09
79E 08
NT
NT
79E 09
79E 09
7 9E 08
NT
1 5E 07
nr
NT
q AF OB
tn
i ;E 09
6 IF 09
nr
nr
35E 09
NT
37E 06
92E 07
9 3E 08
1 IE 05
58E 10
2 7E 07
9 OE-11
NT
NT
NT
NT
NT
NT
NT
NT
53E09
59E08
1 6E 07
87E 09
1 IE-OS
NT
57E09
87E 10
99E07
8 BE 06
29E 07
NT
53E 08
3 IE 08
5 BE 08
54E 09
BSE -07
NT
2 7E 09
3 5F. 08
NT
NT
35E 09
35E 09
3 5E 08
NT
6BF. 08
NT
NT
4 2F. 08
in
76E 10
3 IF. 09
NT
nr
 olume V, Appendu V 14
-------
1
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-------
TABLE 9  Average Inhalation Risks and rioncancoi HQs in Subaica S3
CHEMICAL
Dichlorodifluoromethane
Dichloioalhane. 1.1- (Ethylidene dichlonde)
nichloroothane. 1 .2-
Dichloroethene, 1.1- (Vinylidine chloride)
Dichloroethane (bans), 1.2
Dlchlorophenol, 2.4-
Dichloropropana. 1 ,2- (Propylene dichlonde)
Dichloroptopene (els). 1 3
Dlchloropropsna (trans). 1.3-
Diathylphthalata
Dimathoxybanzldina, 3.3'-
Dimeltiytphenol. 2.4-
Dimethylphttialat*
CM n-butylphthalate
Dlnrbotoluene, 2.6-
Dinrtro-2-methylphenol. 4.6-
Dinrtropheno). 2.4
Dlntbotoluane,2.4-
Dioxana. 1.4-
Dl(n)octyl phthalate
D.2.4-
Ettiytmethacrylate
Ethylbenzene
Ethylena dibromioe
Ethytena oxide
Ethytana thiourea
-luoranthene
-"luorene
-oimaldahyda
"urfural
Heptachtor
feptachlorobiphenyl
Hexachlorobenzene
lexachlorobiphenyl
Hexachlorobutadiana
(exachlorocyclohexane. gamma (Lindane)
-toxachlorocyclopvntadiene
•lexachloroAthane ,
Hexachlorophana
-lexanona. 2-
ndeno(1 .2.3-cd)pyiena
sophorona
/aleic hydruida
^ethoxychlof
dethyt t-butyl ethet
Methyl 2 Pentancne, 4- (MIBK)
delhylene chloride
^ethylnaphthalene. 2-
^onochlorobipbenyl
Naphthalene
litjoanilme 2-
Jitroanilme 3-
Inhalation
Slope
Factor
(mg/kg-d)"-1
NA
NA
9 IE 02
1 2E»00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
7 BE -02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
OOO175
000175
NA
00175
000875
007875
025
000005
NA
OOO007
0035
0035
0175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0 004375
075
002
0 75
NF
NA
0035
OOOO05
NF
Inhalation
RID
(mg/kgd)
1 4E 02
36E 02
NA
2 3E 03
50E 03
75E04
29E 04
1 4E-03
1 4E 03
20E-01
NA
50E 03
NA
2 5E 02
2 5E-04
NF
50E 04
50E-04
NA
50E 03
25E 03
23E 02
7 IE 02
1 4E 05
NA
20E 05
1 OE 02
1 OE 02
50E 02
36E 03
1 3E-04
NA
2 OE-04
NA
50E-05
75E-05
50EO6
2 5E-04
75E 05
NF
NA
50E-02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
tlF
NA
1 OE 02
1 4E 05
NF
Emission
Rate
(g'sec)
25E 04
1 3E 05
3E 05
3E 05
3E 05
55E 06
3E 05
3E 05
3E 05
7E05
2E 04
55E06
55E 06
1 6E 05
55E06
55E 06
55E 06
55E06
4 9E 04
55E08
39E05
2 5E 04
50E04
1 2E 04
31E 05
1 5E 10
55E06
67EO6
6 1E 04
55E 06
55E 07
1 4E 08
55E06
1 4E 08
1 OE 04
55E 05
55E06
55E 06
3 2E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E OS
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
67E 06
Subarea
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
;S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
Adult
Cancer
Risk
NT
NT
1 2E 12
1 5E 11
NT
NT
NT
1 7E 12
1 7E 12
NT
NT
NT
NT
NT
NT
* NT
NT
NT
NT
NT
NT
NT
NT
89E 11
1 IE 11
NT
NT
NT
26E-11
NT
25E-12
NT
90E-12
NT
80E-12
NT
NT
79E-14
NT
NT
NT
NT
NT
NT
NT
NT
6 7E 13
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
29E-12
38E-11
NT
NT
NT
4 IE 12
4 IE 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E 10
27E-11
NT
NT
NT
69E-11
NT
63E-12
NT
23E-11
NT
20E-11
NT
NT
20E 13
NT
NT
NT
NT
NT
tIT
NT
fit
1 7E 12
til
fir
NT
NT
m
School age
Cancer
Risk
NT
NT
1 7E 12
23E 11
NT
NT
NT
25E 12
25E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 10
1 6E-11
NT
NT
NT
42E-11
NT
3 BE 12
NT
1 4E-11
NT
1 2E-11
NT
NT
1 2E-13
NT
NT
NT
NT
NT
tIT
m
NT
1 OF 1 ?
til
m
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
26E 12
34E-11
NT
NT
NT
37E 12
37E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E-10
24E-11
NT
NT
NT
62E-11
NT
56E-12
NT
20E-11
NT
18E-11
NT
NT
1 7E-13
NT
NT
NT
NT
NT
NT
N(
til
1 5F 12
111
NT
NT
NT
til
                                                                                                                                             Adult      Child    School-age  Farmer
                                                                                                                                           Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HQ        HQ
1 4E 07
2 BE 09
NT
44E 08
20E 08
5 BE 08
35E 07
6 9E 08
6 9E 08
67E-10
NT
8 7E-09
NT
50E-09
1 7E-07
NT
8 7E 08
87E-08
NT
87E09
1 2E 07
86E08
55E08
64E-05
NT
58E-11
44E49
53E-09
96EOB
1 2E 08
3 5E-08
NT
22E-07
NT
1 6E-05
5 BE 06
87E06
1 7E 07
34E 06
NT
NT
1 IE 09
73EO9
35E 09
46E 10
1 7E 08
1 5F_ 08
tIT
NT
4 4E 09
3 n 06
tIT
5 IE 07
1 OE 08
NT
1 6E 07
74E 08
2 2E 07
1 3E 06
26E07
26E 07
25E09
NT
33E-08
NT
196 08
65E-07
NT
33E 07
3 3E 07
NT
33E 08
46E07
32E07
2 IE 07
24E04
NT
22E 10
16E 08
20E-08
36E07
46E 08
1 3E-07
NT
8 2E 07
NT
60E 05
22E05
33E 05
65E 07
1 3E 05
NT
NT
40E 09
2 7E 08
1 3E 08
1 7E 09
6 r.E 08
5 r>F 08
NT
nr
1 r,f 08
i 8
87E-08
NT
87E09
12E07
86E48
55Efl8
64E 05
NT
5 BE It
44E^»
53E 09
96E 08
1 2E 08
3 5E 08
NT
2 2E 07
NT
1 6E 05
58E 06
87E 06
1 7E 07
34E 06
NT
NT
1 IE 09
73E 09
35E 09
46E 10
1 7E 08
1 5F 08
NT
NT
44E 09
3 7C OR
III
 olume V  App«ndi» V-'
-------
TABLE 9  Average lnha.-...on Risks and Noncancer HQs in Subarea S3
CHEMICAL
Nitroaniline, 4-
Nitrobenzene
Nittophenol. 2-
Nitrophenol, 4-
N Nilioso-di n-bulylamlne
N-Nitroso-dl-n-propylamlne
N Nltrosodiphenylamlne (Dlphenylamlne)
Nonachloroblphenyt
Octachlorobiphenyl
Pentachlorobenzene
Pentachloroblphenyl
Pentachlor entire-benzene
Pentachlorophencri
Phenanlhrene
Phenol
Pyrana
Safrde (5-(2 Propenyf) 1 .3 benzodioxole)
Styrene
Tetrachtorobtphenyl
Tetrachtoroethane. 1.1.1,2-
Tetrachloroethane. 1.1.2.2-
Tefcachtoroethene
Tetrachtorophenol. 2.3.4.6-
Toluene
Trichloro-1.2.2-trifluoroethane. 1,1,2
Trlchlorobenzen*. 1 ,2.4-
Trfchlorobfphenyl
Trlchloroethane. 1,1,1- (Methyl chloroform)
rrlchloroethane, 1,1. 2-
Trtehloroelhene
Trlchtorofluorornethane
Trtchtorophenol. 2.4.5-
rrtchlorophenol. 2.4,6-
vlnyl acetate
Yinyt chloride
Xylene, m/p- (m/p-Dimethyl benzene)
-------
TAEH E 9  Average Inhalation Risks and tJoncancot MQs in Sub.iifM S3
CHEMICAL
Nitroaniline. 4-
Nitrobenzene
Nibophanol. 2-
Nibophenol, 4-
N Nrboio-di-n-butylamlne
N-Nrboso-4
75E-03
NA
1 5E-01
7 5E 03
NF
7 1E4)2
NA
75E-03
NA
25E 03
75E 03
29E 02
2 1E»00
1 4E-02
NA
7 1E 02
1 OE 03
NA
50E02
25E-02
NA
1 4E-02
NA
50E-01
50E-01
NA
NA
NA
NA
NA
HA
HA
NA
rw
rw
NA
NA
HA
Emission
Rate
(g/sec)
67E 06
55E 06
67E 06
55E 06
1 2E 04
67E-06
67E06
1 4E 08
, 1 4E 08
48E05
1 4E-08
34E-05
55E06
67E 06
55E 06
55E-06
1 2E 04
23E05
1 4E 08
55E 06
55E 06
5 1E 05
68E 06
6 IE 04
3 3E 04
55E-06
30E08
1 3E05
1 3E 05
1 9E 05
25E 04
55E-06
55E 06
64E 05
25E04
3 BE 04
55E-06
108E 11
678E-11
895E 11
166E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subatea
S3avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 «vg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
Adult
Cancel
Risk
NT
NT
NT
NT
67E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E 13
1 IE 12
1 1E-13
NT
NT
NT
NT
NT
NT
73E 13
1 1E-13
NT
NT
56E-14
NT
75E-11
NT
NT
1 7E 12
52E 12
1 4E 12
25E 12
1 7E 12
1 9E 12
94E 13
1 3E 12
26E 12
36E 11
22E 11
20E 11
2 3E-11
Child
Cancet
Risk
NT
NT
NT
NT
1 7E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E 13
2 BE 12
26E 13
NT
NT
NT
NT
NT
NT
1 BE 12
28E-13
NT
NT
1 4E 13
NT
1 9E-10
NT
NT
4 IE 12
1 3E 11
34E 12
63E 12
42E 12
4 7E 12
23E 12
33E 12
66E 12
89E 11
54E 11
5 IE 11
5 7E 11
School age
Cancer
Risk
NT
NT
NT
NT
1 OE-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E 13
1 7E 12
16E-13
NT
NT
NT
NT
NT
NT
1 IE 12
1 7E-13
NT
NT
85E-14
NT
1 1E-10
NT
NT
25E 12
78E 12
2 IE 12
38E 12
25E 12
29E 12
1 4E 12
20E 12
40E 12
54E 11
3 3E 1 1
3 1E 11
35E U
Farmer
Cancel
Risk
NT
NT
NT
NT
1 5E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
32E-13
25E 12
24E-13
NT
NT
NT
NT
NT
NT
1 6E t2
25E-13
NT
NT
1 2E-13
NT
1 7E-10
NT
NT
37E 12
1 2E 11
30E 12
56E 12
37E 12
42E 12
2 IE 12
30E 12
59E 12
79E 11
49E 11
45E 11
5 If 11
                                                                                                                                               Adult      Child   School age  Farmer
                                                                                                                                             Noncancer  Noncancer Noncancei Noncancer
                                                                                                                                                HQ        HQ        HQ        HQ
NT
3 1E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E^)7
5 BE -09
NT
29E-10
58E-09
NT
25EX»
NT
5 BE -09
NT
16E4)7
72E^9
1 7E^)7
12E-09
31EX»
NT
1 4E 09
99E-08
NT
39E08
1 7E4»
NT
36E-08
NT
60EO9
87E-11
NT
NT
NT
NT
NT
NT
NT
tn
m
m
N!
NT
tit
NT
1 1E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 06
2 2E-08
NT
1 IE 09
2 2E-08
NT
93E-09
NT
22E08
NT
6 IE 07
27E 08
64E 07
46E09
1 1E 08
NT
52E09
37E 07
NT
1 5E 07
65E-09
NT
1 3E 07
NT
23E08
33E 10
NT
NT
NT
HT
II!
tn
HT
HI
tn
til
HI
NT
HI
NT
69E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
B IE 07
1 3E-08
NT
66E-10
1 3E-08
NT
56E-09
NT
1 3E-08
NT
3 7E 07
1 6E 08
3 BE 07
28E09
69E-09
NT
31E 09
22E-07
NT
6 BE 08
39E-09
NT
8 1E-08
NT
1 4E 08
20E 10
NT
NT
NT
NT
HT
NT
HT
m
NT
NT
NT
HI
lit
NT
3 1E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E-07
58E-09
NT
29E 10
5 BE -09
NT
25E09
NT
5 BE -09
NT
1 6E 07
72E09
1 7E 07
1 2E 09
31EX)9
NT
1 4E 09
99E-08
NT
39E 08
1 7E-09
NT
36E 08
NT
60E 09
8 7E-11
NT
NT
NT
NT
NT
tn
NT
HT
NT
NT
NT
NT
NT
 >lume V, Appendix V-14
-------
TABLE 9  Average lnho.«iion Risks and Noncancer HQs in Subatea S3
CHEMICAL
1.2.3.7.8.9-HxCDF
1 2,3.46,7.8HpCDF
1 2 3.4 7 8.9 HpCDF
OCDF
Dloxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Parf.culate matter
Respirsble participates
Inhalation
Slope
Factor
(mg/kg-d)M
1 SE+04
1 5E*03
1 5E»03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0675
NA
NA
0000075
00175
0 004375
0004375
0000061
02825
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
' NA
NA

NA
IDE -04
75E-05
36E05
1 3E-03
1 3E-04
1 3E-03
2 5E-01
NA
NA
2 IE 05
50E-03
1 3E 03
1 3E-03
1 8E 05
7 5E-02
SOH^M
UA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
9 30E-09
1 22E 09
1 89E-08
4 28E-08
2 4E-04
42E-06
37E-05
1 5E-04
33E-06
16E-05
7 1E-07
71E^)7
94E-O5
43E-05
1 4E 03
50E-06
47E-04
1 5E-05
34E05
1 2E-04
3 2E-02
24E+00
91E-02
7 2E-02
72E-02
Subarea
S3 avg
S3 avg
S3 ivg
S3 avg

S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
Off-site
Vapor
Cone
(ug/m3)
BSE 12
2 7E-10
35E-11
55E-10
1 2E-09
70E-06
1 2E 07
1 1E-06
44E-06
96E-10
4 6E-07
2 1E-06
2 IE 08
27E06
1 2E-06
4 1E-05
1 5E-07
14E-05
4 4E-07
9 9E-07
35E-06
9 3E-04
7 OE-02
2 6E 03
2 1E-03
2 1E-03
Cancer
Adult
Dose
(mg/kg-d)
30E 16
95E-15
1 2E-15
19E-14
44E-14
25E-10
43E 12
38E-11
1 5E-10
34E-14
1 6E-11
72E-13
72E-13
96E 11
44E-11
14E09
51E-12
48E-10
1 5E-11
35E-11
1 2E-10
33E-08
25E-06
93E08
7 4E-08
74E-08
Cancer
Child
Dose
(mg/kg-d)
75E-16
2 4E-14
3 1E-15
48E-14
1 1E-13
61E-10
1 1E-11
94E-11
38E-10
84E-14
4 1E-11
1 8E-12
1 8E-12
24E-10
1 1E-10
36E-09
13E 11
1 2E-09
38E-11
86E-11
31E-10
8 1E-08
82E-06
2 3E-07
1 8E-07
1 8E-07
Cancer
School-age
Dose
(mg/kg-d)
45E-16
1 4E-14
1 9E-15
29E-14
66E-14
37E-10
6SE-12
57E-11
23E-10
51E-14
25E-11
1 1E-12
1 1E-12
1 4E-10
66E-11
22E-09
7 7E-12
72E-10
23E-11
52E-11
1 8E-10
49E-08
37E-06
1 4E-07
1 1E-07
1 1E-07
Cancer
Farmer
Dose
(mg/kgd)
66E-16
2 1E-14
2 8E-15
43E-14
97E-14
54E-10
95E-12
64E-11
34E-10
75E-14
36E-11
1 6E-12
1 6E-12
2 1E-10
98E-11
32E-09
1 1E-11
1 1E-09
34E-11
77E-11
27E-10
73E-08
55E-06
2 IE 07
1 6E-07
1 6E-07
Noncancer
Adult
Dose
(mgfkgd)
23E-15
7 4E-14
9 7E-15
15E-13
34E-13
19E^)9
33E-11
29E-10
1 2E-09
26E-13
1 3E-10
56E-12
56E-12
75E-10
34E-10
1 1E-08
40E11
37E-09
1 2E-10
27E-10
95E-10
2 5E 07
19E-05
7 2E-07
5 7E-07
5 7E-07
Noncancer
Child
Dose
(mgfltg-d)
87E-15
28E-13
36E-14
S6E 13
1 3E-12
7 1E-09
1 2E-10
1 IE 09
45E-09
9 BE 13
47E-10
21E-11
21E-11
2 BE -09
13E-09
42E-08
1 5E-10
1 4E-00
45E 10
10E-09
36E-09
95E07
72E-05
27E06
2 IE 06
2 1E-06
Noncancer
School-age
Dose
(mg/Vg-d)
53E-15
1 7E-13
22E-14
34E-13
77E-13
43E-09
75E-11
66E-10
27E-09
59E-13
29E-10
13E-11
1 3E-11
1 7E-09
7 7E-10
2 5E-08
90E-11
84E-09
27E-10
6 IE 10
22E-09
57E4)7
43E05
1 6E 06
1 3E-06
1 3E-06
Noncancer
Farmer
Dose
(mg/Vgd)
23E-15
74E-14
97E-15
15E-13
34E-13
19E-09
33E-11
29E-10
12E^»
26E 13
1 3E-10
56E-12
56E-12
75E10
34E-10
1 1E-08
40E-11
37E-09
1 2E-10
2 7E 10
95E-10
25E07
19E4S
7 2E-07
57E-07
5 7E-07
NOTES:
  NA - Not applicable
  NF-Not found      *-
  NT • No toxicKy information
  HQ - Hazard quotient
  HI - Hazard Index
/olume V. Appendix V-14
-------
TABLE 9  Aveiage Inhalation Risks and Moncancei HOs m Stibaipa S3
CHEMICAL
1 2 3.7,8 9 HxCDF
1 2 346 7.8HpCDF
1. 2.3,4.7.8.9 HpCDF
OCDF
Dioxln TEd
Aluminum
Antimony
Arsanlc
Barium
Beryllium
Cadmium
"hromlum (hexavalenl)
Chromium (bivalent)
"oppet
_ead
Mercury (and MeHg)
Mickel
Selenium
Silver
Thallium
'Jnc
tydrogan chloride
'obi nitrogen oxides (NOx)
'ot»l sulfur oxides (SOx)
'articulate matter
(esplrable participates
Inhalation
Slope
Factor
(mg/kg d)*-1
1 5E+04
1 5E»03
1 5E»03
1 5E»02

NA
NA
50
NA
64
6 1
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000436
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
1 OE 04
75E 05
36E 05
1 3E 03
1 3E 04
1 3E 03
25E 01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E 03
1 8E 05
75E 02
50E 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E 10
930E 09
1 22E 09
1 89E 08
4 28E-08
24E 04
,42E-06
3 7E 05
1 5E 04
33E 06
1 6E^5
7 1E-07
7 IE 07
94E 05
4 3E4>5
1 4E 03
50E06
4 7E 04
1 5E 05
34E 05
1 2E 04
32E 02
2 4E»00
9 1E 02
72E 02
72E 02
Subarea
S3 avg
S3avg
S3 avg
S3 avg

S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 evg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
S3 avg
Adult
Cancer
Risk
45E 12
1 4E 11
1 9E 12
29E 12
1 4E 10
NT
NT
1 9E-09
NT
26E 13
10E-10
30E-11
NT
NT
NT
NT
43E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancef
Risk
1 IE 11
35E 11
4 7E 12
7 2E 12
36E 10
NT
NT
4 7E 09
NT
7 1E-13
25E 10
74E-11
NT
NT
NT
NT
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
68E 12
2 1E-11
28E 12
44E-12
22E-10
NT
NT
2 BE 09
NT
43E 13
1 5E 10
45E-11
NT
NT
NT
NT
65E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Faimer
Cancer
Risk
1 OE 11
32E-11
4 2E 12
64E-12
32E 10
NT
NT
4 2E 09
NT
63E-13
22E 10
66E-11
NT
NT
NT
NT
95E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
 IOTES
  NA - Not applicable
  NF - Not found
  NT - No toxicity Information
  HO * Hazard quotient
  HI = Hazard index
                                                                                Total Risk   32E09    7 9E 09    4 BE 09    7 IE 09
                                                                                                                                               Adult      Child    School-age  Faimoi
                                                                                                                                             Noncancef Noncancer Noncancer Noncancei
                                                                                                                                                HQ       HQ       HQ       HQ
NT
NT
NT
NT
NT
NT
33E-07
39E-06
33E-05
2 IE 10
1 OE-06
45E 09
23E-11
NT
NT
5 2E 04
79E09
30E 06
95E 08
1 5E 05
1 3E 08
5 1E-04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 06
1 5E 05
1 2E 04
7 BE 10
38E 06
1 7E-08
84E-11
NT
NT
1 9E 03
30E 08
1 IE 05
3 6E 07
58E05
4 7E 08
1 9E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
7 5E 07
8 BE 06
75E-05
47E 10
23E-06
1 OE-08
5 1E-11
NT
NT
1 2E 03
1 8E 08
67E<)6
22E4)7
35E-05
29E-08
1 1E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E 07
39E 06
3 3E 05
2 IE 10
1 OE 06
4 5E 09
23E-11
NT
NT
52E 04
79E 09
30E06
95E 08
1 5E 05
1 3E 08
5 1E-04
NT
NT
NT
NT
                                                                                                                                     Total HI    1 2E-03    46E-03    2 8E 03    1 2E-03
     e V Appendi* V
-------
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-------
TABIE 10  Aveiage Inhalation Risks and Noncancpi HQs in Subaiea Wl
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acelophenone
Acrylonitrile
Anthracene
Benzene
Benzole acid
Benzotrichloride
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranlhen*
Benzo(g,h.l)perylene
Benzo(k)fluoranlhene
Bis(2 chloroethoxy) methane
Bls(2-chloroethyl)ether
Bls(2-chlorolsopropyl)ether
Brs(2-ettiylhexy1)phthalate
Bromodichloromethane
Bromoform
Bromomethane
Brornodiphenyl ether, p-
Butanone, 2- (Methyl ettiyl kelone)
Butylbenzytphthalale
Carbon dlsulflde
Carbon tetrachloride
Chlordane
Chloro-3-methylphenol 4
Chloroaniline. p- (4-Chloroanilme)
Chlorobenzene
Chlorobenzilate
Chloroethane (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthalene. beta
Chlorophenol, 2-
Chlorodiphenyl ether, 4-
Chrysene *:
Cresol. m
Cresol. o- (2-Methylphenol)
Cresol. p-
Crotonaldehyde
3umene
3DE.4.4
>berxz(a.h)anthracene
Dibromochloromethane
Dichlorobenzene, 1 3
Dichlorobenzene, 1 4
3ichlorobenzene. 1,2-
lichloioben/idme 3 3'
"hchlof obiphenyl
Inhalation
Slope
Factor
(mg/kg d)*-1
NA
NF
7 7E-03
NA
NA
24E 01
NA
2 9E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
3 9E 03
NA
NA
NA
NA
NA
5 3E 02
1 3E»00
NF
NA
NA
2 7E-01
NA
8 1E 02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0 004375
NA
000225
NA
NA
00175
NA
02
005
NA
MA
Inhalation
RfD
(mg/kg d)
1 5E 02
NF
64E 04
25E 02
25E 02
1 4E 04
7 5E-02
4 3E-04
1 OE»00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E 03
50E 03
36E 04
NA
7 IE 02
50E 02
7 IE-04
1 4E 04
1 5E-05
NF
1 OE 03
1 4E-03
50E 03
7 1E 01
25E 03
NA
20E 02
1 3E 03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
6 4E 04
NA
NA
5 OF. 03
NA
57E 02
1 4E 02
HA
HA
Emission
Rate
(g/sec)
6 7E 06
6 7E 06
30E 04
29E 03
29E-04
20E 04
55E-06
1 5E 05
1 IE 05
32E-05
55E 08
55E-08
55E-06
55E-06
55E-06
67E 06
1 3E 05
67E 06
37E 05
1 OE 04
55E 06
49E*4
6 7E 06
5 IE 05
55E-06
89E 05
1 6E 04
5 5E-07
6 7E-06
6 7E 06
55E06
37E-05
49E-04
2 7E 04
25E 04
67E-06
55E 06
67E-06
55E 06
55E-06
55E-06
55E 06
1 4E 04
55E 06
55E O/
55E 06
26E 05
55E 06
55E 06
55E 06
3 3E 05
4 7E 08
Subaiea
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
Wt ivg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wt avg
Wl avg
Wt avg
W1 avg
Wt avg
Wl avg
Wl avg
Wt avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
Wt avg
Wl avg
W1 avg
Wl avg
Wl avg
Wt avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
/'Wl avg
Wl avg
Wl avg
Wl avg
Wt avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Adult
Cancer
Risk
NT
NT
1 6E 11
NT
NT
34E-10
NT
30E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 OE-10
NT
NT
NT
1 5E-13
NT
NT
NT
NT
NT
59E-11
50E-12
NT
NT
NT
71E-11
NT
1 5E-10
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HI
Child
Cancer
Risk
NT
NT
4 IE 11
NT
NT
84E-10
NT
75E-12
NT
NT
NT
NT
NT
NT
NT
NT
26E-10
NT
NT
NT
37E-13
NT
NT
NT
NT
NT
1 5E 10
1 2E-11
NT
NT
NT
1 8E-10
NT
38E-10
27E-11
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
NT
NT
NT
NT
NT
tn
School age
Cancer
Risk
NT
NT
25E 11
NT
NT
5 1E-10
NT
45E 12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
22E-13
NT
NT
NT
NT
NT
88E-11
76E-12
NT
NT
NT
1 1E-10
NT
23E-10
1 6E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
tn
NT
NT
NT
NT
Ml
til
HI
Farmer
Cancer
Risk
NT
NT
36E-11
NT
NT
75E 10
NT
67E-12
NT
NT
NT
NT
NT
NT
NT
NT
23E-10
NT
NT
NT
33E-13
NT
NT
NT
NT
NT
1 3E-10
1 1E-11
NT
NT
NT
1 6E-10
NT
34E-10
24E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
NT
                                                                                                                                                Adult      Child   School age  Faimei
                                                                                                                                              Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                                 HQ       HQ        HQ        HQ
2 4E-08
NT
2 6E 05
64E 06
6 4E 07
77E05
40E09
1 9E-06
62E-10
NT
NT
NT
NT
NT
NT
NT
NT
3 7E 08
4 1E-07
1 IE 06
60E-08
75E-05
NT
39E08
60E 09
68E06
6 1E05
20E06
NT
3 7E 07
2 IE 07
40E07
3 BE 08
58E-06
NT
1 BE -08
24E07
NT
NT
24E^)8
24E-08
24E-07
NT
47E-07
NT
NT
2 9F. 07
NT
5 3E 09
? tF. no-
rn
NT
9 IE-OS
NT
96E 05
2 4E-05
24E 06
29E 04
15E 08
70E06
23E 09
NT
NT
NT
NT
NT
NT
NT
NT
1 4E 07
1 5E 06
42E06
2 3E 07
2 8E-04
NT
1 5E 07
2 3E 08
26E 05
23E 04
75E 06
NT
1 4E 06
79E 07
15E 06
1 4E 07
2 2E 05
NT
6 BE 08
90E 07
NT
NT
90E 08
90E 08
90E 07
NT
1 8F 06
NT
m
1 tl 06
NT
2 Of 08
7 HI 08
IIT
m
5 5E 08
NT
58E 05
1 4E 05
1 4E 06
1 7E 04
9 IE 09
42E 06
1 4E-09
NT
NT
NT
NT
NT
NT
NT
NT
8 3E 08
9 2E 07
26E 06
1 4E 07
1 7E-04
NT
89E 08
1 4E 08
1 5E 05
1 4E 04
45E-06
NT
83E07
48E 07
9 IE 07
85E 08
1 3E 05
NT
4 1E 08
54E 07
NT
NT
54E 08
54E 08
54E 07
NT
1 1F. 06
NT
NT
6 SF 07
m
1 2E 08
4 BE 08
NT
m
2 4E-08
NT
26E 05
64E 06
64E 07
7 7E 05
40E 09
1 9E 06
62E-10
NT
NT
NT
NT
NT
NT
NT
NT
3 7E 08
4 IE 07
1 IE 06
6 OE 08
75E05
NT
39E08
60E 09
68E 06
6 IE 05
2 OF. 06
NT
3 7E 07
2 IE 07
40E 07
3 BE 08
5 BE 06
NT
1 8E 08
2 4E 07
NT
NT
24E 08
24E 08
2 4E 07
NT
4 7E 07
NT
NT
? 9E 07
NT
5 3E 09
2 IE 08
NT
m
'olume V  Appendix V-1 *
-------
TABLE 10  Average Inhalation Risks and Noncancei HOs in Subaiea W1
CHEMICAL (
Dichlorodrfluoromethane
Dlchloroethan*. 1.1- (Ethylidene dichloride)
Dlchloroethane. 1.2-
Dtchloroethen*. 1,1- (Vmylidlne chloride)
Dichloroethene (bans). 1 .2-
Dichlorophenol, 2.4-
Dichloropropane. 1 ,2- (Propylene dichtotide)
Dtchloropropene (cis). 1 .3-
CHchkxopfopene (bans). 1 .3-
Diethylphlhalate
Dimethoxybenzldine. 3,3'-
Dtmethylphenol. 2.4-
OirmthytphthaM*
Dl-n-butylphthalate
Dinrtrotoluene. 2.6-
Drn»ro-2-metnytpn«nol. 4.6-
Dinrtrophenol. 2.4-
Dinttrotoiuene, 2.4-
Diox»n». 1.4-
Dl(n)octyl phthalate
D. 2,4-
Eltiyl melhacrylate
Ethylbenzene
Etfiylene dlbromlde
Ethylene oxide
Ethytene thlourea
Fluoranthene
Fluofene
Formaldehyde
Furfural
Heptachkx
Heptachlofoblphenyl
Hexachlorobenzene
Hexachloroblphenyt
Hexachtorobutadiene
Hexachtorocyclohexane. gamma (LIndan*)
Hexachtorocyctopentadleto
Hexachloroe thane
Hexachlofophene
Hexanone, 2-
lndeno(1 .2,3-cd)pyrene
Isophoron*
Maleic hydrazide
Methoxychlor
Methyl-l-butyl ether
Methyl 2-Pentanone, 4 (MIBK)
Methylene chloride
Methylnaphthalene, 2-
Monochloroblpheny!
Naphthalene
Nitroaniline. 2-
Nitroaniline. 3-
Inhalation
Slope
Factor
mg/kg-d)A-
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
16E+00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
N*
NF
RAC
(mg/m3)
005
0125
NA
0 007875
00175
0002625
0001
0005
0.005
07
NA
00175
NA
0.0675
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0175
0.0125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
OO04375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RfD
(mg/kg-d)
1 4E-02
36E-02
NA
2 3E-03
5 OE-03
75E-04
29E-04
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
2 5E-02
25E-04
NF
50E04
50E-04
NA
5 OE-03
25E-03
2 3E 02
7 IE 02
1 4E-05
NA
2 Oc-05
1 OE-02
1 OE-02
5 OE-02
3 6E-03
1 3E-04
NA
2 OE-04
NA
50E-05
75E-05
50E-08
2 5E-04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 1E 01
5 7E 03
2 1E-01
NF
NA
1 OE 02
1 4E 05
NF
Emission
Rate
(g/sec)
25E-04
3E^)5
3E05
3E-05
3E-05
55E-06
3E4W
3E05
3E-05
7E-05
2E-04
55E-00
556-06
16E05
55E-06
55E-06
55E06
55E-06
49E-04
55E06
39E-05
2 5E-04
50E^)4
1 2E-04
3 IE-OS
1 5E-10
55E-06
67E-06
8 1E-04
55E4W
5 5E-07
1 4E-08
55E-06
1 4E-08
1 OE-04
55E-05
55E-06
55E-06
32E-05
6 4E-05
55E-06
6 7E 06
1 2E 04
55E07
1 3E 05
1 3E 05
40E 04
4 2E 05
1 7E 08
5 5E 06
67E 06
6 7E 06
Subarea
W1 avg
WI avg
WI avg
W1 avg
WI avg
WI avg
Wt avg
WI avg
WI avg
WI avg
WI avg
WI avg
Wlavg
Wt avg
W1 avg
Wlavg
WI avg
WI avg
WI avg
W1 avg
WI avg
WI avg
WI avg
WI avg
WI avg
Wt avg
WI avg
WI avg
WI avg
WI avg
W1 avg
WI avg
WI avg
Wt avg
WI avg
WI avg
WI avg
Wt avg
Wt avg
WI avg
Wt avg
Wt avg
W1 avg
W1 avg
WI avg
WI avg
WI avg
WI avg
Wt avg
WI avg
WI avg
Wt avg
Off-site
Vapor
Cone
(ug/m3)
49E-05
25E06
25E-06
25E-06
25E-06
1 1E-06
25E-06
25E-06
25E-06
34E-06
23E-05
1E-06
1E-06
1E-06
IE 06
1E-06
1E06
1E-06
99E-05
1 1E-06
78E-06
4 9E-05
1 OE-04
23E-05
61E-06
29E II
1E-06
3E-06
2E-04
1E-06
1E-07
28E09
1 1E-06
28E09
2 OE-05
1 IE-OS
1 1E-06
1 1E-06
64E-06
1 3E-05
1 IE 06
1 3E 06
23E 05
1 IE 07
25E 06
25E 06
79E 05
84E 06
33E 09
1 IE 06
1 3E 06
1 3E 06
Cancer
Adult
Dose
(mg/kg-d)
1 7E-09
88E-11
88E-1I
88E-11
88E-11
39E-11
88E-11
88E-11
88E-11
1 2E-10
81E-10
39E-11
39E-11
1 1E-10
39E-11
39E-11
39E-11
39E-11
35E-09
39E-11
27E-10
1 7E-09
35E-09
81E-10
2 IE 10
10E-15
39E-11
47E-11
43E-09
39E-11
39E-12
99E-14
39E-11
99E-14
7 1E-10
39E-10
39E-11
39E-11
23E-10
45E-10
39E-11
4 7E 11
81E-10
39E 12
88E 1t
88E 11
28E 09
29E 10
1 2E 13
39E 11
4 7E 11
4 7E-1I
Cancer
Child
Dose
(mg/kg-d)
4 3E 09
22E-10
22E 10
22E-10
22E-10
96E-11
22E-10
22E 10
22E-10
30E-10
20E-09
96E-11
96E-11
2 7E-10
96E-11
96E-1I
96E1I
96E-11
8 7E-09
96E-11
68E-10
43E-09
87E-09
20E-09
54E-10
26E-15
96E-11
1 2E-10
1 1E-08
96E-11
96E-12
25E-13
96E-11
25E-13
1 8E-09
96E-10
96E-11
96E-11
56E-IO
1 IE 09
96E-11
1 2E 10
20E 09
96E 12
22E 10
22E 10
69E 09
7 3E 10
29E 13
96E 11
1 2E 10
t 2E 10
Cancer
School-age
Dose
(mg/kg-d)
26E-09
3E-10
3E-10
3E-10
3E-10
58E-11
3E-10
3E-10
3E-10
8E-10
2E-09
5BE-11
58E-11
1 7E-10
58E-11
58E-11
58E-11
5 BE 1 1
52E-09
S8E-11
4 IE 10
26E-09
53E-09
1 2E-09
32E-10
1 5E-15
58E-11
7.1E-11
64E-09
58E-11
58E-12
1 5E-13
5 8E-1 1
1 5E-13
1 1E-09
58E-10
58E-11
58E-11
34E-10
68E-10
58E-11
7 IE 11
1 2E 09
58E 12
1 3E-10
1 3E 10
4 2E 09
44E 10
1 BE 13
5 BE 11
7 IE 11
7 IE-It
Cancer
Farmer
Dose
(mg/kg-d)
3 8E-09
20E-10
20E-10
20E-10
20E-10
86E-11
20E-10
20E-10
20E-10
26E10
18E-09
86E-11
86E-11
25E-10
86E-11
86E-11
86E-11
86E-11
7 7E-09
86E-11
61E-10
38E-09
7 BE -09
18E-09
4 8E-10
23E-15
86E-11
1 OE-10
95E-09
86E-11
86E-12
22E-13
86E-11
22E-13
16E09
86E-10
86E-11
86E-11
5 OE-10
1 OE-09
86E-11
1 OE-10
1 BE -09
86E 12
20E 10
20E 10
62E 09
65E 10
26E 13
86E 11
1 OE 10
1 OE (0
Noncancer
Adult
Dose
(mg/kg-d)
1 3E-08
68E-10
6 BE- 10
68E-10
68E-10
3 OE-10
6 BE 10
68E-10
68E-10
92E-10
63E-09
3 OE-10
3 OE-10
86E-10
3 OE-10
30E 10
3 OE-10
3 OE-10
2 7E-08
3 OE-10
21E-09
1 3E-08
2 7E 08
63E09
17E-09
eoE-ts
3 OE-10
37E-10
3 3E-OB
30E10
30E-11
77E-13
3 OE-10
77E 13
55E-09
3 OE-09
3 OE-10
30E 10
1 8E-09
35E-09
3 OE-10
37E 10
63E09
30E 11
6 BE 10
6 BE 10
22E 08
23E 09
9 IE 13
30E 10
3 7E 10
3 IF 10
Noncancer
Child
Dose
(mg/kg-d)
50E-08
26E09
26E-09
26E09
26E-09
1 1E-09
26E-09
26E09
26E-09
35E-09
24E-OB
1E-09
1E-09
2E-09
1E-09
IE 09
1E-09
1E-09
OE07
11E^»
79E-09
50E08
10E07
24E-08
62E-09
30E-14
1 IE 09
1 4E-09
1 2E 07
1 1E-09
1 tE-10
29E 12
1 IE 09
29E 12
2 IE 08
1 IE 08
1 IE 09
1 IE 09
65E09
1 3E08
1 IE 09
t 4E 09
24E 08
1 1E 10
26E 09
26E 09
8 1E 08
86E 09
34E 12
1 IE 09
t 4E 09
t 4E 09
Moncancer
School-age
Dose
(mg/kg-d)
3 OE 08
1 5E-09
1 5E-09
1 5E-09
15E-09
68E-10
15E-09
15E-09
15E09
21E-09
1 4E 08
68E-10
6 BE tO
19E-09
68E-10
6 BE tO
68E-10
68E-10
61E^)8
68E-10
4 BE 09
3 OE 08
6 2E 08
1 4E-OB
3 BE 09
t BE 14
68E-10
83E-10
75E08
6 BE 10
6 BE 11
1 7E 12
6 BE 10
1 7E 12
1 2E 08
6 BE 09
6 BE 10
68E-10
4 OE-09
80E 09
6 BE 10
83E 10
14E08
68E 11
1 5E 09
1 5E 09
49E 08
52E 09
2 1E 12
6 BE 10
83E 10
83E 10
Moncancet
Farmer
Dose
(mg/kgd)
1 3E-08
68E-10
6 BE 10
6 BE 10
6 BE 10
30E 10
6 BE 10
66E-10
6 BE 10
92E10
63E-09
30E 10
30E 10
66E-10
3 OE-10
30E-10
30E-10
30E-10
27E^)S
30E-10
21E-09
13E46
2 7E 08
63E09
1 7E-09
BOE-15
30E 10
37E-10
33E4B
3 OE-10
30E 11
77E-13
30E 10
77E 13
55E^>9
30E09
30E-10
30E 10
t 8EXI9
35E-09
30E 10
37E 10
83E4)9
30E 11
6 BE 10
68E 10
22E 08
23E 09
9 IE 13
30E 10
3 7E 10
3 7f 10
Volume V. Appendix V-14
-------
TABI E  10  Aveiage Inhalation Rr,l4
NA
2 OE-04
NA
50E 05
7 5E 05
50E 06
2 5E 04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 1E 01
NF
NA
1 OE 02
1 4E-05
t)F
Emission
Rate
(g/s«c)
2 5E 04
1 3E 05
1 3E 05
1 3E 05
1 3E 05
55E-06
3E-05
3E-05
3E-05
7E-05
2E-04
55E06
55E06
1 6E 05
55E-06
55E06
55E-06
556-06
49E-04
55E 06
3 9E-O5
25E04
5 OE-04
1 2E-04
3 1E 05
1 5E-10
55E-06
67E-06
6 1E 04
55EO6
55E 07
1 4E 08
55E-06
1 4E 08
1 OE-04
5 5E-05
55E06
5 5E-06
32E 05
64E 05
55E 06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
67E 06
6 7E 06
Subarea
Wl avg
Wl avg
W1 avg
Wl avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wt avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
Wl avg
Wt avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
Wl avg
W1 avg
Wl avg
Wl avg
W1 avg
Wt avg
Wl avg
Wl avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wt avg
W1 avg
Adult
Cancer
Risk
NT
NT
80E 12
1 1E-10
NT
NT
NT
1 1E-11
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
62E 10
75E 11
NT
NT
NT
1 9E-10
NT
1 7E-11
NT
62E-11
NT
55E-11
NT
NT
54E-I3
NT
NT
NT
NT
NT
NT
NT
in
46E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
20E-11
26E 10
NT
NT
NT
28E 11
286-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
t 5E 09
1 9E-10
NT
NT
NT
48E-10
NT
43E-11
NT
1 6E-10
NT
14E-10
NT
NT
1 4E 12
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 11
m
NT
NT
NT
NT
School age
Cancer
Risk
NT
NT
1 2E 11
16E-10
NT
NT
NT
1 7E 11
1 7E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
93E-10
1 1E-10
NT
NT
NT
29E 10
NT
26E-11
NT
94E-11
NT
64E-11
NT
NT
82E-13
NT
NT
NT
NT
NT
NT
NT
m
69E 12
tIT
in
in
in
tit
Farmer
Cancer
Risk
NT
NT
1 BE- 11
2 3E-10
NT
NT
NT
25E-11
25E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
14E09
1 7E-10
NT
NT
NT
43E-10
NT
39E-11
NT
1 4E-10
NT
1 2E-10
NT
NT
1 2E-12
NT
NT
NT
NT
NT
NT
in
in
i or 11
(IT
HT
fIT
in
tIT
                                                                                                                                                Adult      Child    School age   Faimer
                                                                                                                                             Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                                 HQ        HQ        HQ        HQ
94E 07
1 9E 08
NT
30E07
1 4E 07
4 OE 07
24E 06
4 8E-07
4 BE -07
46E-09
NT
60E-08
NT
34E08
1 2E 06
NT
60E07
60E-07
NT
6 OE 08
8 5E 07
60E-07
38E-07
4 4E 04
NT
40E-10
30E-08
3 7E-06
6 6E 07
8 4E 08
2 4E-07
NT
1 SE-06
NT
1 1E-04
40E05
60E 05
12E06
2 3E 05
NT
NT
73E 09
50E08
24E 08
32E 09
t 2E 07
1 OF 07
NT
in
3 OF 08
?6f 06
III
35E 06
7 2E 08
NT
1 IE 06
5 IE 07
1 5E 06
90E 06
18E-06
18E-06
17E-08
NT
2 3E-07
NT
1 3E 07
45E-06
NT
23E06
23E-06
NT
2 3E 07
32E06
22E06
1 4E 06
1 6E-03
NT
15E09
1 IE 07
14E07
25E 06
32E07
90E 07
NT
56E-06
NT
4 IE 04
1 5E 04
23E 04
45E06
8 7E 05
NT
NT
2 7E 08
1 9E 07
9 OF 08
1 2E 08
4 5F 07
i nr n?
tit
NT
i ir o?
9 r,r m
tn
2 IE 06
43E 08
NT
69E-07
3 IE 07
91E-07
S4E 06
1 IE 06
1 IE 06
10E-08
NT
1 4E^)7
NT
7 7E 08
2 7E 06
NT
4E 06
4E4)6
NT
4E^)7
9E06
3E 06
86E07
10Efl3
NT
90E 10
6 BE 08
83E08
15E06
1 9E 07
54E 07
NT
34E06
NT
25E 04
90E05
1 4E 04
2 7E 06
53E 05
NT
NT
1 7E 08
1 IE 07
5 4E "08
7 2E 09
2 7E 07
2 IE 07
NT
til
68E 08
sir ns
111
94E 07
1 9E 08
NT
30E 07
1 4E 07
40E 07
24E06
48E 07
4 BE 07
46E-09
NT
6 OE-08
NT
34E08
1 2E 06
NT
60E07
60E 07
NT
60E 08
BSE 07
60E 07
3 BE 07
4 4E 04
NT
40E 10
30E 08
3 7E 08
66E 07
84E 08
24E 07
NT
1 5E 06
NT
1 IE 04
40E 05
60E 05
1 2E 06
23E 05
NT
NT
73E 09
50E 08
24E 08
32E 09
1 ?E 07
1 nr o?
tit
HI
30E 08
26r m
in
 olume V, Appendix V-M
-------
TABLE 10  Average Inhalation Risks and Noncancer HQs in Subaiea W1
CHEMICAL
Nitroaniline, 4-
Nitrobenzene
Nitrophenol. 2-
Nrtrophenol. 4-
N NHioso-dl-n-butylamlne
N-NHioso-dl-n-piopylamine
N-NHrosodfphenylamlne (Diphenyfamine)
Nonachlofobiphenyt
Octachlorobiphenyl
Pentachtofobenzene
Pentachlorobiphenyl
PentachtoronHrobanzene
Pentachlorophenol
Phenanlhiene
Phenol
Pyrene
Safrole (5-(2-Propenyl)- 1 ,3-benzodioxole)
Stytene
Tetrachloroblphenyt
Tetrachloroethane. 1,1.1,2
Tetrachloroelhane. 1,1.2.2-
Tetrachloroethene
Tetrachlofophenol. 2.3.4.6- -
Toluene
TrtehlofO-1.2.2-trinuoroethane. 1.1.2-
Trkhbrobenzene. 1.2,4-
Trlchtocoblphenyl
Trkhloroethane. 1.1.1- (Methyl chloroform)
TrfchtoroelhBne. 1.1.2-
Trichloroethene
Trtchlorofluoromethane
Trfchlorophenol. 2.4.5-
Tricnforophenol. 2.4.6-
Vinyl acetate
Vinyl chloride
Xytone, m/p- (m/p-Dlmettiy) benzene)
Xylene, o- (o-Dimethyl benzene)
2.3.7.8-TCDD
1.2.3,7.8-PCDO
1.2.3.4.7.8-HxCDD
1.2.3.6.7.B-HxCDO
1.2.3,7.8,9-HxCDD
1. 2.3,4.6.7.8 HpC DO
OCDO
2.3.7.8 TCDF
1,2.3. 7.8 PCDF
2,3.4.7.8 PCDF
1.2.3 4.7.8 HxCDF
1,2, 3 6.7. 8 HxCDF
2,3.4.6.7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg-oT-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E02
20E-01
206-03
NA
NA
NA
NA
NA
NA
57E^)2
60E-03
NA
NA
tOE-02
NA
30E-01
NA
NA
1 5E»05
75E+04
1 5E+04
1 5E+04
1 5E+04
5E+03
5E+02
5E+04
5E+03
5E»04
5E»04
5E»04
5E+04
RAC
(mg/m3)
NF
00005
NF '
NF
NA
NA
NA
NA
NA
NA
NA
0002825
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
0 1
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
75E-03
NF
71E-02
NA
75E-03
NA
2 5E-03
75603
29E-02
2 1E»00
1 4E^2
NA
7 IE 02
10E-03
NA
50E02
2 5E-02
NA
1 4E-02
NA
50E01
50E01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E-06
55E-06
1 2E-04
67E-06
67E-06
'1 4E-08
14E-08
4 BE -05
14E-08
34E-05
55E06
67E-06
55E-06
55E-08
1 2E-04
23E05
1 4E-08
55E-06
55E-06
51E05
6 BE -08
81E04
33E-04
55E06
30E-08
1 3E-05
1 3E-05
19E-OS
2 5E 04
55E-08
55E-08
64E-05
2 5E-04
3 BE 04
55E-06
1 08E-11
676E-11
895E-11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
3 45E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subatea
Wl ivg
W1 avg
Wl ivg
Wl *vg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wlavg
Wl avg
Wl avg
Wlavg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wt avg
Wl avg
Wl avg
Wlivg
Wt avg
Wt avg
Wl avg
Wl avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wtivg
W1 avg
Wl avg
Wt avg
Wl avg
Wl avg
Wt avg
W1 avg
Wl ivg
Wl vg
Wl vg
Wl vg
Wl vg
Wl vg
Wl vg
Wl vg
Wl vg
W1 vg
on site
Vapor
Cone
(ug/m3)
1 3E-06
1 1E-06
1 3E-06
1 1E-06
24E-05
1 3E 06
1 3E-08
2 BE 09
28E-09
95E-08
2 BE 09
67E-06
1 1E-06
1 3E 06
1 1E-06
1 1E-06
23E-05
45E-06
28E-09
1 IE-OS
1 1E-06
10E-05
14E-06
1 2E-04
66E-05
1 1E-06
60E09
25E06
25E06
37E-06
4 9E-05
1 IE 06
t IE 06
1 3E 05
49E-05
76E-05
1 1E-06
22E-12
1 4E 11
1 BE 11
33E-11
22E 11
25E-10
1 2E 09
1 BE- 11
69E 11
93E 11
29E 10
2 7E 10
30E 10
Cancer
Adult
Dose
(mg/kg-d)
47E-11
39E-11
47E 11
39E-11
85E-10
47E-11
47E-11
99E-14
99E-14
34E-10
99E-14
24E-10
39E-11
47E-11
39E-11
39E-11
81E-10
1 6E-10
99E-14
39E-11
3 9E-1 1
36E-10
48E-11
43E-09
23E-09
39E-11
2 1E-13
88E-11
8 BE 11
1 3E-10
17E-09
39E-11
39E-11
45E-10
1 7E-09
27E-09
39E-11
76E-17
48E-16
63E 16
12E 15
7 7E 16
8 7E 15
43E 14
62E 16
24E 15
33E 15
1 OE 14
94E 15
1 1E-14
Cancer
Child
Dose
(mg/kg-d)
1 2E-10
96E-11
1 2E 10
96E-11
21E-09
1 2E-10
1 2E-10
25E-13
25E-13
84E-10
25E-13
59E-10
96E-11
1 2E-10
96E-11
96E-11
20E-09
3 9E-10
25E-13
96E-11
96E-11
90E-10
1 2E-10
1 1E-08
58E-09
96E-11
53E-13
22E10
22E-10
33E-10
43E-09
96E-11
96E-11
1 1E-09
43E-09
67E-09
96E-11
1 9E-16
1 2E-15
1 6E-15
29E-15
1 9E 15
22E 14
1 1E-13
1 5E 15
60E 15
82E 15
25E 14
23E 14
26E 14
Cancer
School-age
Dose
(mg/kg-d)
7 1E-11
58E-11
71E-11
58E-11
1 3E-09
71E-11
71E-11
1 5E-13
1 5E-13
50E-10
1 5E-13
36E-10
58E-11
71E-11
58E-11
58E-11
12E-09
2 4E-10
1 5E-13
58E-11
58E-11
54E-10
72E-11
85E-09
35E-09
58E-11
32E-13
1 3E-10
1 3E-10
20E-10
26E-09
5BE-11
58E-11
68E-10
26E-09
40E-09
S8E-11
1 1E-16
72E-16
95E-16
1 BE 15
1 2E 15
1 3E 14
65E 14
93E 16
3 7E 15
49E 15
1 5E 14
1 4E-14
1 6E 14
Cancer
Farmer
Dose
(mg/kg-d)
1 OE-10
B6E 11
1 OE-10
B6E-11
19E-09
1 OE-10
10E-10
22E-13
22E-13
74E-10
22E-13
53E-10
86E-11
1 OE-10
86E-11
B6E-11
18E-09
35E-10
22E-13
86E-11
B6E-11
8 OE-10
1 1E-10
96E-09
52E-O9
86E-11
47E-13
20E-10
2 OE-10
29E-10
38E-09
86E 11
86E-11
10E4W
38E-09
60E-09
86E-11
7E-16
1E-15
4E-15
6E-15
7E-15
9E 14
96E 14
1 4E 15
54E 15
73E 15
22E 14
2 IE 14
2 IE 14
Noncancer
Adult
Dose
(mg/kg-d)
37E-10
3 OE-10
37E-10
3 OE-10
66E-09
37E-10
3 7E-10
77E-13
77E-13
26E-09
7.7E-13
18E-09
3 OE-10
37E 10
3 OE-10
3 OE-10
63E-09
12E-09
77E-13
30E-10
3 OE-10
28E-O9
37E-10
34E-C8
18E-08
3 OE-10
1 7E-12
68E-10
6 BE 10
10E-09
1 3E-OB
3 OE-10
30E-10
35E-09
13E-08
2 IE 08
3 OE-10
59E 16
37E 15
49E-15
9 IE-IS
60E 15
6 BE 14
34E 13
48E 15
1 9E 14
26E 14
7 BE 14
7 3E 1 4
82E 14
Noncancer
Child
Dose
(mg/kgd)
1 4E-09
1 1E-09
14E-09
1 1E-09
2 5E-08
1 4E-09
14E-09
29E-12
29E-12
97E-09
29E 12
69E09
1 1E 09
1 4E-09
1 1E-09
1 1E4»
24E08
46E09
29E-12
1 1E-O9
1 1E-09
10E-08
14E-09
13E4)7
6 BE -08
1 1E-09
62E-12
26E09
26E-09
38E09
50E08
1 1E 09
1 IE 09
1 3E-08
5 OE 08
7 BE 08
1 1E-09
22E 15
1 4E 14
1 8E 14
34E 14
2 2E 14
25E 13
1 3E 12
1 8E-14
7 IE 14
96E 14
29E 13
2 7E 13
3 IE 13
Noncancer
School-age
Dose
(mg/kgd)
83E-10
68E-10
83E-10
66E-10
1 5E-OB
83E-10
83E-IO
1 7E-12
1 7E-12
59E-09
1 7E-12
42E09
68E 10
83E-10
6BE-10
68E-10
1 4E-08
2 BE -09
1 7E-12
6 BE 10
6BE-10
63E09
84E-10
7 6E-08
4 1E-08
68E-10
37E-12
1 5E-09
15E09
23E-09
30E08
68E-10
6 BE- 10
8 OE 09
3 OE 08
4 7E-08
6BE-10
1 3E 15
84E 15
1 IE 14
20E 14
1 3E 14
1 5E 13
- 76E 13
1 IE 14
43E 14
5 BE 14
1 BE 13
1 7E 13
1 9E 13
•loncancei
Farmer
Dose
(mg/kg-d)
37E-10
3 OE-10
37E-10
3 OE-10
66E-09
37E-10
37E-10
77E-13
77E 13
26E-09
77E-13
1BE-09
3 OE-10
37E 10
3 OE-10
3 OE-10
63E-09
12E-09
77E-13
3 OE-10
30E 10
28E-09
37E-10
34E-08
18E08
30E-10
1 7E 12
68E-10
68E-10
10E09
1 3E-08
30E 10
30E-IO
35E09
1 3E 08
2 IE 08
30E-10
59E 16
37E 15
49E 15
9 IE 15
60E 15
6 BE 14
34E 13
48E 15
1 9E 14
26E 14
7 BE 14
73E 14
82E 14
 /olume V. Appendix V-14
-------
TABLE  10  Average Inhalation Risks and Moncancpr MQs in Subaiea W1
CHEMICAL
Nftroaniline. 4-
Nitrobonzene
Nitrophenot, 2-
Nitrophenol. 4-
N NrtToso-di n-butylamin*
N-Nitroso-dl n-propylamine
N Nitrosodiphenytamlne (Diphenylamine)
Nonichlorobiphenyl
Octachlorobiphenyl
Pentachlorobenzen*
Pentachlorobiphenyl
Pentachloronrtrobenzene
Pentachlorophenol
Phananthrena
Phenol
Pytena
Saffole (5-(2-PropenyT)-1.3 benzodioxoie)
Slyrana
Telrachloroblphenyl
Tebachloroettiana. t.1.1 2-
Tetrachloroethanc. 1.1.2.2-
Tetrachloroethene
Tetrachloiophenol. 2.3.4.6-
Toluane
Trlchloro-t.2.2-tril1uoroethane. 1 12
Trlchloroberuene. 1.2,4-
Tilcniorobiplianyl
Trlchlocoethane. 1.1.1- (Methyl chloroform)
Trlchloroethane, 1.1,2-
Trichloioathena
Tnchloronuoromethana
Ttichlotophenol. 2.4.5-
Trichlorophanol. 2.4,6-
Vlnyl acetala
Vinyl chloride
Xylene, m/p- (nVp Dimethyl benzene)
Xylan* , o- (o-Dimathyl benzene)
2.37.8TCDD
.2.3.7.BPCDD
2347 8 HxCDO
2.3 6.7,8 HxCDD
,2,3,7 8.9 HxCDD
2 3.4 6.7,8-HpCDD
OCDD
23.7.8 TCDF
1237 8 PCDF
2347 8 PCDF
1 2 3 4 7.8 HxCDF
123678 H«CDF
234678 H.CDF
Inhalation
Slope
Factor
(mg/kg-d)* 1
NF
NA
NF
NF
54E*00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
20E 01
20E 03
NA
NA
HA
NA
NA
NA
57E 02
60E-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E+05
7 5E+04
1 5E+04
1 5E+04
1 5E*04
1 5E»03
1 5E + 02
1 5E»04
75E»03
75E«04
1 5E»04
1 5E»04
1 5E*04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
002625
NA
OOO875
002625
0 1
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E-04
75E 03
NA
1 5E 01
7 5E-03
NF
7 1E-02
NA
75E-03
NA
25E-03
75E 03
29E-02
2 1E»00
1 4E 02
NA
7 IE 02
1 OE-03
NA
50E 02
25E-02
NA
1 4E 02
NA
50E 01
50E 01
NA
NA
NA
NA
NA
NA
NA
NA
MA
tJA
MA
NA
MA
Emission
Rate
(g/sec)
67E 06
55E 06
67E 06
55E 06
1 2E 04
67E06
67E06
1 4E 08
1 4E^»
48E05
1 4E-06
34E-05
55E06
67E46
55E^»
55E^)6
1 2E 04
2 3E-05
1 4E-08
55E46
55E06
5 1E 05
68EO6
6 IE 04
33E 04
55EO6
30E08
1 3E-05
1 3E 05
1 9E Ob
25E 04
55E-06
55E4)6
64E 05
2 5E 04
38E 04
55E-06
1 08E-11
678E-11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 1 5E 09
8 77E 11
3 46E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
Wt avg
W1 avg
W1 avg
W1 avg
W1 avg
Wt avg
Wt avg
W1 avg
W1 avg
Wf avg
W1 avg
Wt avg
Wt avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
Wt avg
W1 avg
W1 avg
W1 avg
Wt avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
Wt avg
Wt avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
W1 avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Adult
Cancer
Risk
NT
NT
NT
NT
46E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 OE 12
79E 12
73E 13
NT
NT
NT
NT
NT
NT
50E 12
78E-13
NT
NT
39E-13
NT
52E-10
NT
NT
1 1E-11
36E 11
95E 12
1 7E 11
1 2E -11
1 3E 11
65E 12
9 3F 12
1 BE 11
2 5E 10
1 5E 10
1 4E 10
1 6E 10
Child
Cancer
Risk
NT
NT
NT
NT
1 1E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E 12
20E 11
1 BE 12
NT
NT
NT
NT
NT
NT
1 2E 11
1 9E 12
NT
NT
96E 13
NT
1 3E 09
NT
NT
28E 11
89E 11
24E 11
4 4E 11
29E 11
3 3E 11
1 6E 11
2 3E 11
45E 11
6 IE 10
38E 10
35E 10
40E 10
School age
Cancer
Risk
NT
NT
NT
NT
69E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E 12
1 2E It
1 IE 12
NT
NT
NT
NT
NT
NT
76E 12
1 2E-12
NT
NT
58E-13
NT
78E-10
NT
NT
1 7E 11
54E 11
1 4E 11
26E 11
1 7E 11
20E 11
9 BE 12
1 4E 11
2 7E 11
3 7E 10
2 3F 10
2 IE 10
2 4F 10
Farmer
Cancer
Risk
NT
NT
NT
NT
1 OE-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E 12
t 7E 11
1 6E 12
NT
NT
NT
NT
NT
NT
1 IE 11
1 7E-12
NT
NT
86E-13
NT
1 2E-09
NT
NT
25E-11
BOE 11
2 IE 11
39E 11
26E 11
29E 11
1 4E 11
2 1E 11
4oe u
55E 10
3 3E 10
3 IE 10
1 c,f 10
                                                                                                                                              Adult     Child    School age  Farmer
                                                                                                                                            Noncancer Noncancer Noncancer Noncancar
                                                                                                                                               HQ       HQ       HQ       HQ
NT
2 1E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E06
4 OE-08
NT
20E-09
40E08
NT
1 7E-08
NT
4 OE-08
NT
1 IE 06
50E08
1 2E-06
84E-09
2 IE 08
NT
96E09
6 BE 07
NT
2 7E 07
1 2E-08
NT
25E-07
NT
4 2E 08
60E 10
NT
NT
NT
NT
NT
NT
NT
m
in
m
m
in
m
NT
79E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
92E06
1 5E-07
NT
75E 09
1 5E-07
NT
64E-08
NT
1 5E 07
NT
42E 06
19E07
44E 06
32E08
79E 08
NT
36E 08
26E06
NT
t OE 06
45E08
NT
9 2E-07
NT
16E 07
23E 09
NT
MT
NT
m
riT
rn
lit
til
in
in
in
in
rn
NT
4 8E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
56E 06
9 IE-OS
NT
45E 09
9 IE-OB
NT
39E-OB
NT
9 IE-OB
NT
25E 06
1 1E 07
27E06
1 9E4B
4 BE 48
NT
22E 08
15E06
NT
6 IE 07
27E 08
NT
56E 07
NT
94E 08
1 4E 09
UT
lit
lit
MT
MT
lit
Ml
MT
MI
MT
MT
MT
MI
NT
2 IE 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E06
4 OE-OB
NT
20E 09
4 OE 08
NT
1 7E-08
NT
4 OE-OB
NT
1 IE 06
50E 08
12E06
84E 09
2 IE 08
NT
96E 09
6 BE 07
NT
2 7E 07
1 2E 08
NT
2 5E 07
NT
42E 08
60E 10
NT
NT
NT
MI
III
NT
NT
UT
tit
m
Mf
MT
MT
/olume V Append'* V 1
-------
TABLE 10  Averagel
,'on Risks and Noncancer HQs in Subarea Wl
CHEMICAL
1 2 3.7 8 9 HxCDF
1. 2.3.4.6.7.8 HpCDF
1.2.3.4.7.8.9-HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trlvalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Sliver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Particulate matter
Resptrable particulars
Inhalation
Slope
Factor
(mg/kg-d)"-t
1 5E+04
1 5E+03
1 5E»03
1 5E»02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
004
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0 004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E-05
36E-05
1 3E-03
1 3E-04
1 3E 03
25E-0)
NA
NA
2 1E 05
5 OE 03
1 3E-03
1 3E^)3
1 BE 05
75E-02
50E-04
NA
^
NA
NF
Emission
Rate
(g/sec)
2 93E-10
930E09
1 22E 09
1 89E 08
428E-08
24E-04
42E-06
37E-05
1 5E-04
33E-08
16E^»
7 1E-07
7 1E-07
94E-05
43E-05
1 4E 03
50E-06
47E-04
15E-05
34EX>5
1 2E-04
32E^)2
24E»00
91E-02
72E-02
72E-02
Subarea
W1 avg
Wl avg
W1 avg
Wt avg

Wl ivg
W1 avg
Wt avg
Wt avg
Wlavg
Wt avg
Wt avg
Wt avg
Wt ivg
Wl ivg
Wt avg
Wt avg
Wt avg
Wl avg
Wt avg
W1 avg
W1 avg
Wl avg
Wt avg
Wl avg
Wt avg
Off-site
Vapor
Cone
(ug/m3)
59E-11
t 9E 09
2 4E-10
3 BE 09
86E 09
48E-05
84E07
74E 06
30E05
66E-09
32E-06
1 4E-07
1 4E 07
19E 05
B6E 06
2 8E -04
1 OE 06
94E05
30E-06
68E-06
24E-05
6 4E-03
4 8E-OI
1 BE -02
1 4E-02
1 4E-02
Cancer
Adult
Dose
(mg/kg-d)
2 IE 15
66E 14
86E-15
1 3E-13
30E-13
1 7E-09
30E-11
26E-10
1 1E-09
23E-13
t 1E-10
50E-t2
50E 12
66E-IO
30E-10
99E-09
35E-tt
33E09
t 1E-10
24E-10
BSE 10
23E-07
1 7E-05
64E 07
5 1E-07
5 1E-07
Cancer
Child
Dose
(mg/kg-d)
5 IE-IS
t 6E 13
2 IE 14
33E-13
75E 13
42E 09
74E 11
65E-10
26E09
58E-13
28E-10
1 2E-11
12E tl
1 6E-09
75E-10
2 5E-08
8 BE 11
82E-09
2 6E-10
60E-10
2 1E-09
5 6E-07
42E-05
t 6E-06
1 3E 06
1 3E 06
Cancer
School age
Dose
(mg/kg-d)
3 1E-15
99E 14
1 3E 14
20E 13
45E-13
25E-09
45E-11
39E-IO
16E-09
35E-13
1 7E-10
75E-12
75E-12
1 OE-09
46E-10
15E-08
53E-11
5 OE-09
16E-10
36E-10
1 3E-09
34E-07
26E^)5
96E4»
7 6E-07
7 6E-07
Cancer
Farmer
Dose
(mg/kg-d)
4 6E-15
1 5E-13
1 9E-14
30E-13
67E-13
3 BE -09
66E-11
S8E-10
23E-09
52E-13
25E-IO
1 1E-11
t IE-It
t SE-09
67E-10
22E^)8
78E-11
74E-09
23E-10
53E-10
1 9E-09
50EX)7
3 BE -05
1 4E-06
t 1E-06
1 1E-06
Noncancer
Adult
Dose
(mg/kg-d)
t 6E-14
5 IE-13
67E-14
1 OE-12
23E t2
t 3E-08
23E-10
2 OE-09
8 2E-09
1 BE 12
88E-10
39E-11
39E-11
5 IE 09
24E-09
7 7E-08
2 7E-10
2 6E-08
82E-10
1 9E-09
66E-09
1BE-06
13E-04
50E-06
39E-06
39E-06
Noncancer
Child
Dose
(mg/kg-d)
60E-14
t 9E 12
25E-13
39E-12
88E-I2
4 9E 08
86E 10
76E-09
31E08
68E-12
33E-09
1 5E-10
1 5E 10
t 9E-08
8 BE -09
2 9E-07
1 OE-09
96E-08
3 1E-09
70E09
25E-08
65E-06
50E-04
19E-05
1 5E 05
1 5E-05
Noncancer
School-age
Dose
(mg/kg-d)
36E-14
t 2E-12
1 5E-13
23E-12
53E-12
30E-08
52E-10
46E-09
1 9E-08
4 IE 12
2 OE-09
88E-11
88E-M
1 2E-08
53E-09
1 7E-07
62E-10
5 BE 08
t 9E-09
42E^)9
t 5E-08
40E-06
30E-04
1 1E 05
89E-06
89E-06
Noncancer
Farmer
Dose
(mg/kg-d)
1 6E-14
51E-t3
67E 14
IDE 12
23E 12
t 3E 08
23E-10
2 OE 09
8 2E-09
18E 12
88E-10
39E-11
39E-11
51E-09
2 4E-09
7 7E 08
2 7E-10
2 6E-OB
82E-10
19E09
66E-09
t 8EO6
1 3E-04
50E-06
39E06
39E06
NOTES.
  NA - Not applicable
  NF« Not found
  NT > No toxlcrty inrbrmaUon
  HQ • Hazard quotient
  HI -Hazard index
Volume V. Appendix V-14
-------
TABLE  10  Average Inhalation Risks and Noncancer MQs in Subaioa V\M
CHEMICAL
12 3 7 8,9HxCDF
1.23 4.6.7.8 HpCDF
1 2 34 78.9 HpCOF
OCDF
Oioxm TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (Irivalenl)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
fine
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
^articulate matter
^espirable particulates
Inhalation
Slope
Factor
(mg/kg d)A-1
1 5E«04
1 5E«03
1 5E»03
1 5E»02

NA
NA
50
NA
84
6 1
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0004375
0875
NA
NA
OOOO075
00175
0004375
OOO4375
OOOOO61
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
10E 04
75E 05
36E 05
1 3E 03
1 3E 04
1 3E 03
25E01
NA
NA
2 1E 05
50E 03
1 3E 03
1 3E 03
1 BE 05
7 5E 02
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E 09
1 22E 09
1 89E 08
428E.08
24E 04
4 2E 06
37E 05
1 5E 04
33E 08
1 6E^)5
7 IE 07
7 IE 07
94E 05
4 3E 05
1 4E 03
50E 06
4 7E-04
1 5E-05
34E 05
1 2E-04
32E-02
2 4E+00
9 1E^>2
72E 02
7 2E-02
Subarea
W1 avg
W1 avg
W! avg
Wl avg

W1 ivg
W1 avg
W1 ivg
Wl avg
W1 avg
Wl avg
Wl avg
W1 avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
Wl avg
W1 avg
W1 avg
Wl avg
Wl avg
W1 avg
W1 avg
Wl avg
Adult
Cancer
Risk
3 IE-It
9 BE 11
1 3E 11
20E-11
99E 10
NT
NT
1 3E4)8
NT
20E 12
69E 10
20E-10
NT
NT
NT
NT
30E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
7 7E 11
2 4E 10
32E 11
50E 11
25E 09
NT
NT
32E-08
NT
49E-12
1 7E 09
5 IE 10
NT
NT
NT
NT
74E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
4 7E 11
1 5E 10
1 9E 11
30E 11
1 5E 09
NT
NT
2 OE-08
NT
29E 12
t OE 09
3 IE 10
NT
NT
NT
NT
45E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
69E-11
2 2E 10
29E 11
44E 11
22E 09
NT
NT
2 9E-08
NT
43E 12
1 5E 09
46E-10
NT
NT
NT
NT
66E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                               Adult      Child    School-age   Farmer
                                                                                                                                             Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                HQ        HO       HQ       HQ
NT
NT
NT
NT
NT
NT
23E06
2 7E 05
23E 04
1 4E 09
70E06
3 IE 08
1 6E-10
NT
NT
36E-03
5 5E 08
2 1E^)5
66E4J7
1 IE 04
8 BE -08
3 5E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
86E 06
1 OE 04
8 6E 04
54E 09
2 6E 05
1 2E 07
58E-10
NT
NT
1 3E 02
2 OE 07
77E 05
25E 06
40E04
33E07
1 3E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
52E 06
6 IE 05
52E 04
33E 09
1 6E-05
70E 08
35E-IO
NT
NT
8 IE 03
1 2E 07
4 7E 05
I 5E 06
24E 04
20E 07
7 9E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
23E-06
27E05
2 3E 04
I 4E 09
70E^)6
3 1E 08
1 6E-10
NT
NT
36E4)3
55E^)8
2 IE 05
66E47
1 1E^)4
8 BE 08
35E-03
NT
NT
NT
NT
                                                                                Total Risk   22E-08    5 5E-08    3 3E-08    4 9E-08
                                                                                                                                     Total HI   85E03    32E-02    1 9E 02    8 5E 03
NlOTES
  NA - Not applicable
  NF • Not found
  NT = No toxicity information
  HO * Hazard quotient
  HI - Hazard index
 olume V. Appendix V-M
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                                                                                                   i
                                                       f—
                                                       m
-------
TABLE 11  Average Inhalation Rr.ks and Noncancer HQs in Subarca W2
CHEMICAL
Acenaphttiene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrylonrbile
Anthracene
Benzene
Benzole acid
Benzotrlchloride
Benzo(a)anthracene
B»nzoja)pyren«
Beruo(b)nuoranthene
Benzo(g,n,l)perylene
Benzo(k)fluoranthene
Bls(2-chlofoethoxy) methane
Bls(2-chloroethyl)ether
Bis(2 -chlotoisopr opyl)ether
Bis(2-«ttiylnein/ijphthala!e
3tomodichloromethan«
Uromoform
3romomethane
3romodiphenyl ether p
3utanon», 2- (Methyl ethyl kelone)
3utylb«r\rylphthalate
:arbon disulfide
"atb^n lettachloride
^hlordane
vhloro-3-methylphenol. 4
Ihloroaniline. p- (4-Chloroaniline)
:hlorob«nzene
:i,/orobenzilate
^hloioettiane (Ethyl chloride)
Chloroform
:hlotomethane
^hloronaphthalene. beta
;hlorophenol. 2-
xhlotodiphenyl ether, 4-
;hrysene *;
^resol, m-
:resol, o- (2-Methylphenol)
:iesol, p.
'.rotonaldehyde
'.umene
>DE,4.4'-
>ibenz(a ,h>antht acene
)ibromochloromelhane
Jichlorobenzene 1,3-
lichlorobenzene. 1 4
lichloiobenzene. 1.2-
)ichlorobenzidme. 3.3 -
Jichloiobiphenyl
Inhalation
Slope
Factor
(mg/kg d)*-1
NA
NF
7 7E-03
NA
NA
24E 01
NA
2 9E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E»00
NF
NA
NA
2 7E-01
NA
8 IE 02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA '
NA
NA
RAC
(mg/rr>3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
f4A
NA
Inhalation
RID
(mg/kg d)
1 5E-02
NF
64E 04
25E 02
25E 02
1 4E 04
75E 02
43E 04
1 OE*00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E^)3
50E 03
36E 04
NA
7 IE 02
50E 02
7 1E 04
1 4E 04
1 5E 05
NF
1 OE 03
1 4E 03
50E 03
7 1E 01
25E-03
NA
20E 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
64E 04
NA
NA
50E 03
NA
5 7E 02
1 4E 02
tIA
NA
Emission
Rate
(g/sec)
67E06
67E-06
3 OE 04
29E 03
29E04
20E 04
55E08
1 5E-05
,1 IE 05
32E05
55E06
55E06
55E06
55E06
55E06
67E06
1 3E 05
6 7E06
3 7E 05
1 OE 04
55E 06
4 BE 04
6 7E 06
5 IE 05
55E06
89E 05
1 6E 04
55E07
67E-06
67E06
55E 06
3 7E 05
49E 04
2 7E 04
25E 04
6 7E-06
55E-06
67E 06
55E-06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2»vg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2tvB
W2tvg
W2avg
W2 ivg
W2avg
W2ivg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2 avg
W2avg
W2 avg
W2avg
W2 avg
W2 avg
W2avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 avg
Adult
Cancer
Risk
NT
NT
78E 12
NT
NT
1 6E-10
NT
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
49E 11
NT
NT
NT
72E 14
NT
NT
NT
NT
NT
2 BE 11
24E-12
NT
NT
NT
34E-11
NT
72E 11
52E-12
NT
NT
NT
NT
NT
NT
NT
m
NT
in
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
20E 11
NT
NT
40E 10
NT
36E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-10
NT
NT
NT
1 8E-13
NT
NT
NT
NT
NT
TOE 11
60E-12
NT
NT
NT
85E-11
NT
1 8E-10
1 3E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
til
NT
NT
m
NT
School-age
Cancer
Risk
NT
NT
1 2E 11
NT
NT
24E 10
NT
22E-12
NT
NT
NT
NT
NT
NT
NT
NT
74E-11
NT
NT
NT
1 1E-13
NT
NT
NT
NT
NT
42E 11
36E 12
NT
NT
NT
5 1E-11
NT
1 IE 10
79E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
m
(IT
m
m
Farmer
Cancer
Risk
NT
NT
1 7E 11
NT
NT
36E-10
NT
32E 12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
16E-13
NT
NT
NT
NT
NT
62E 11
54E-12
NT
NT
NT
75E-11
NT
1 6E-10
12E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
ur
Nt
NT
NT
NT
NT
111
NT
                                                                                                                                             Adult      Child   School age   Farmer
                                                                                                                                          Noncancer Noncancer Noncancer Noncancer
                                                                                                                                             HQ       HO       HO       HO
1 2E 08
NT
1 2E 05
30E 06
3 IE 07
3 7E 05
1 9E 09
90E-07
30E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 8E 08
20E 07
5 4E-07
29E 08
36E-05
NT
1 9E 08
29E-09
33E06
29E-05
96E-07
NT
1 BE 07
1 OE 07
1 9E 07
1 8E 08
28E-06
NT
8 BE 09
1 2E-07
NT
NT
1 2E 08
1 2E 08
1 2E 07
NT
2 2E 07
NT
NT
1 4E 07
m
2f)E 09
1 flE 08
til
Ml
44E 08
NT
46E 05
1 1E 05
1 2E 06
1 4E 04
7 2E 09
34E 06
1 1E-09
NT
NT
NT
NT
NT
NT
NT
NT
66E 08
73E 07
20E06
1 1E 07
1 3E-04
NT
7 1E 08
1 IE 08
1 2E 05
1 IE 04
36E 06
NT
66E 07
3 BE 07
72E 07
6 7E 08
1 OE-05
NT
3 3E 08
4 3E 07
NT
NT
43E 08
4 3E OB
43E-07
NT
8 4E 07
NT
NT
5 ?[ 07
m
9 5E 09
3 flf 08
(IT
NT
26E-08
NT
28E 05
69E 06
70E-07
8 4E-05
4 4E 09
20E-06
67E-10
NT
NT
NT
NT
NT
NT
NT
NT
40E-08
4 4E-07
1 2E 06
65E08
81E-05
NT
43E 08
65E 09
74E 06
66E 05
22E 06
NT
40E 07
2 3E 07
44E 07
4 IE 08
63E 06
NT
20E 08
26E 07
NT
NT
26E 08
26E 08
26E 07
NT
5 IF 07
NT
NT
3 IE 07
NT
5 7E 09
? IF 08
(IT
111
1 2E-08
NT
1 2E-05
30E 06
3 IE 07
3 7E 05
19E09
90E 07
30E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 BE 08
20E 07
54E07
29E 08
36E 05
NT
1 9E 08
29E 09
33E 06
29E 05
96E 07
NT
1 BE 07
1 OE 07
1 9E 07
1 BE 08
2 BE 06
NT
8 BE 09
1 2E-07
NT
NT
1 2E 08
1 2E 08
1 ?E 07
NT
22E 07
NT
I4T
1 4E-07
NT
25F 09
1 OE 08
m
NT
 olume V. Appendix V-14
-------
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TABLE  ' t  Average Inhalation Risks and Nonrancoi HO5 in Subaipa W2
CHEMICAL
Dichlorodrtluofomethane
Dichloroethane. 1 1 (Ethylidene dichloride)
Dichloroethane. 1,2-
Dichloroettiena. 1.1- (Vmylidine chlonde)
Dichloroethene (lians), 1.2-
Dichloroph«nol.2,4-
Dichloropropan*. 1 .2 (Propylene dichloride)
Oichloropropene (crs), 1.3-
Dtchloropropen* (bans). 1.3-
Diethylphthalate
Dimethoxybenztdlne. 3.3'-
Dim«thytphenol. 2,4-
Dim»thy1phttialale
Oi-n-butylphlhalal*
Olnrtjotoluena. 2.6-
Dinrtro-2-methylphenol. 4 6-
Dintoophenol. 2.4-
Dinitiotolu»n», 2.4-
Dioxane. 1.4-
Di(n)octy1 phlhalala
D. 2.4-
Ethyt metnacrylate
Elhytbenzene
Elhytene dibiomide
Ethytene oxide
Ithytene thiourea
7luorantfi«ne
rluorane
ormaldehyde
"uifural
leptachlor
leptachloroblphenyl
(exachlorobenzene
taxachlorobiphenyl
Hexachlorobutadiene
Iflxachlorocyclohexane, gamma (Lindane)
lexachlorocyclopentadiene
toxachloroethane
iexachlorophene '-
fexanone, 2-
ideno(1.2.3-cd)pytene
sophorone
laleic hydrazide
lelhoxychlor
lelhyl 1- butyl ether
lethyl 2 Penlanone. 4 (MIBK)
lelhylane chloride
lethylnaphthalene, 2-
tonochloiobiphenyl
laphtfialene
litfoanihne 2-
htioamline 3
Inhalation
Slope
Factor
(mg/kg d)A-1
NA
NA
9 1E 02
1 2E*00
NA
NA
NA
1 3E4)1
1 3E 01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
45E 02
NA
45E+00
NA
1 6E+00
NA
7 BE 02
NA
NA
1 4E 02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E 03
NF
NA
NA
NA
NF
RAG
(mg/m3)
005
0 125
NA
0007875
00175
0002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
OD175
000875
007875
025
OOOO05
NA
OOOO07
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0 000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
000005
NF
Inhalation
RtD
(mg/kg d)
1 4E 02
3 6E-02
NA
23E 03
50E 03
7 5E 04
29E 04
1 4E 03
1 4E^>3
20E-01
NA
506-03
NA
25E 02
25E-04
NF
SOE 04
50E-04
NA
SOE 03
25Efl3
2 3E 02
7 1E 02
1 4E 05
NA
20E 05
1 OE 02
1 OE 02
SOE 02
36E 03
1 3E 04
NA
2 OE-04
NA
SOE -05
75E 05
SOE 06
25E 04
75E 05
NF
NA
SOE 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E 05
(If
Emission
Rate
(g'sec)
2 5E 04
1 3E 05
1 3E 05
1 3E 05
1 3E 05
55E06
1 3E 05
1 3E 05
, 1 3E OS
1 7E 05
1 2E 04
55E06
55E06
1 6E 05
55E 06
55E 06
55E 06
55E 06
49E 04
55E-06
39E 05
25E 04
SOE 04
1 2E 04
3 IE 05
1 5E 10
55E 06
67E 06
6 IE 04
55E 06
55E 07
1 4E 08
55E-06
1 4E-08
1 OE 04
55E 05
55E 06
55E 06
32E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E W
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
W2 avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2«vg
W2avg
W2avg
W2 avg
W2 avg
W2avg
W2avg
W2avg
W2 tvg
W2avg
W2avg
W2 avg
W2tvg
W2avg
W2avg
W2ivg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2 avg
W2 avg
W2 avg
W2avg
W2 avg
W2avg
W2 avg
W2 avg
W2 avg
W2avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 a«g
W2 avg
W? avg
Adult
Cancel
Risk
NT
NT
38E 12
5 1E-11
NT
NT
NT
55E 12
55E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E 10
36E-11
NT
NT
NT
92E 11
NT
84E 12
NT
30E-11
NT
2 7E 11
NT
NT
26E-13
NT
NT
NT
NT
NT
NT
NT
tJT
? 2E 12
(IT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
96E 12
1 3E-10
NT
NT
NT
1 4E 11
1 4E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
74E 10
90E 11
NT
NT
NT
23E 10
NT
2 1E-11
NT
75E-11
NT
66E-11
NT
NT
65E-13
NT
NT
NT
NT
NT
NT
NT
m
S'.F 12
NT
NT
NT
NT
tu
School age
Cancel
Risk
NT
NT
5 BE 12
76E It
NT
NT
NT
82E 12
82E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
44E 10
54E-11
NT
NT
NT
1 4E-10
NT
1 3E-11
NT
45E-11
NT
40E 11
NT
NT
39E 13
NT
NT
NT
NT
tJT
NT
NT
NT
3 3F 12
III
NT
Nl
HI
III
Farmer
Cancer
Risk
NT
NT
85E-12
1 IE 10
NT
NT
NT
1 2E 11
1 2E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
66E 10
BOE 11
NT
NT
NT
2 1E-10
NT
1 9E-11
NT
67E-11
NT
59E-11
NT
NT
58E-13
NT
NT
NT
NT
NT
NT
NT
NT
49F 1?
m
NT
NT
IJ1
IH
                                                                                                                                                Adult      Child   School age   Farmer
                                                                                                                                             Noncancer Noncancei Noncancei Noncancef
                                                                                                                                                HQ       HQ       HQ       HQ
45E-07
92E-09
NT
1 5E 07
66E 08
1 9E 07
1 2E 06
2 3E 07
2 3E 07
22E 09
NT
2 9E-08
NT
1 6E-08
5 8E-07
NT
29E07
2 9E-07
NT
29E08
4 IE 07
29E 07
1 8E 07
2 1E-04
NT
1 9E 10
1 4E 08
1 BE 08
32E 07
4 OE 08
1 2E 07
NT
72E-07
NT
53E05
1 9E 05
29E 05
5 BE 07
1 1E-05
NT
NT
35E 09
24E 08
1 2E 08
1 5E 09
58E 08
4 9E 08
tir
tu
1 4E Ou
t 2F 05
m
1 7E 06
34E 08
NT
55E07
25E07
72E 07
43E 06
86E 07
86E07
B3E 09
NT
1 1E^)7
NT
62E-08
22E 06
NT
1 IE 06
1 1E-06
NT
1 1E 07
1 5E06
1 IE 06
89E^7
79E04
NT
72E 10
54E 08
66E08
1 2E 06
1 5E 07
4 3E 07
NT
27E-06
NT
20E 04
7 2E 05
1 IE 04
22E 06
4 2E 05
NT
NT
1 3E 08
9 OE 08
4 3F. 08
5 7F 09
2 1F 07
1 Bl m
tit
Nt
5 4f 08
4 fif Or,
Nt
1 OE 06
2 IE-OS
NT
33E 07
1 5E 07
44E 07
26E-06
52E-07
52E07
SOE 09
NT
6 5E 08
NT
3 7E 08
1 3E 06
NT
65E07
6 5E-07
NT
65E 08
92E07
65E07
4 IE 07
4 BE -04
NT
43E 10
33E 08
40E 08
72E 07
9 IE 08
2 6E 07
NT
1 6E 06
NT
1 2E 04
43E05
65E 05
1 3E 06
2 5E 05
NT
NT
79E 09
55E 08
26F 08
35E 09
1 IF 07
1 IF 07
IIT
NT
3 )f 08
2 BF 05
IH
45E 07
92E 09
NT
1 5E 07
66E 08
1 9E 07
1 2E 06
2 3E-07
2 3E 07
22E 09
NT
29E-08
NT
1 6E 08
5 8E-07
NT
2 9E 07
29E-07
NT
29E08
4 IE 07
29E 07
1 BE 07
2 1E-04
NT
1 9E 10
1 4E 08
1 BE 08
3 2E 07
40E 08
1 2E 07
NT
7 2E-07
NT
53E 05
19E 05
29E 05
5 BE 07
1 IE 05
NT
NT
35E 09
24E 08
1 2E 08
1 5F 09
5 BE 08
4 IF 08
NT
NT
1 4F 08
1 2F 05
til
     e V  Appendix V-14
-------
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-------
TABl E  11  Average Inhalation Riski and Noncancei MQs in Suharea W2
CHEMICAL
Nilroanilme. 4-
NilJobenzene
Nilrophonol, 2-
Niliophenol, 4-
N Nrtrojo-di-n-butylamlne
N Nrhoso-di-n-propylamine
N Nrtrosodiphenylamine (Diphenylamine)
Nonachloroblphenyl
Octachhxoblphenyl
Pentachlorobenzene
Pentachloroblphenyl
Penlachloronitrobenzane
Pentachloropnenol
Phenanthrene
"henol
'yrene
Saliole (5-(2-Ptop«nyl)-1 .3 bfltuodioxole)
Styrene
Tetrachlorobiphenyl
[•(rachloioethan«. 1.1.1.2-
fetrachloroethane. 1.1.2.2
retrachloroethene
!etcachloioph«nol. 2.3.4.6
oluene
2
NA
SOEfll
50EX)1
NA
NA
NA
NA
NA
NA
tJA
NA
NA
NA
NA
NA
MA
Emission
Rate
(g'sec)
67E-06
55E-06
6 7E-06
55E 06
1 2E-04
67E-06
67E-06
1 4E 06
, 1 4E-08
48E-05
1 4E 08
34E-05
55E-06
87E^>6
55E^)6
55E 06
1 2E04
23E 05
1 4E 08
55E-06
55E 06
5 IE 05
68E06
6 1E^)4
33E 04
55E^)6
30E-08
1 3E*5
13E^)5
1 9E 05
25E4)4
55EO6
55E 06
64E 05
2 5E-04
38E-04
55E-06
1 08E-11
678E 11
895E-H
1 66E-10
1 09E 10
1 24E 09
6 15E 09
677E -11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
W2 avg
W2avg
W2avg
W2 avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
W2 avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2 avg
W2 avg
W2avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 avg
W2 avg
W? avg
Adult
Cancer
Risk
NT
NT
NT
NT
2 2E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
48E 13
38E 12
35E-13
NT
NT
NT
NT
NT
NT
246-12
37E-13
NT
NT
1 9E-13
NT
25E-10
NT
NT
55E 12
1 7E-11
45E 12
84E 12
55E-12
63E 12
3 1E-12
44E 12
8 7E 12
1 2E 10
7 2E 11
68E 11
76E It
Child
Cancer
Risk
NT
NT
NT
NT
55E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 12
94E 12
88E-13
NT
NT
NT
NT
NT
NT
60E-12
93E-13
NT
NT
46E-13
NT
62E-10
NT
NT
1 4E 11
43E-11
1 1E-11
2 IE 11
1 4E 1 1
1 6E (1
78E 12
1 IE 11
22E 11
29E 10
1 BE 10
1 7E 10
1 9E 10
School age
Cancer
Risk
NT
NT
NT
NT
3 3E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
72E 13
57E 12
53E-13
NT
NT
NT
NT
NT
NT
36E 12
56E 13
NT
NT
28E-13
NT
3 7E-10
NT
NT
82E-12
26E 11
68E 12
1 3E 11
63E 12
95E 12
4 7E 12
6 7E 12
1 3E 11
1 8E 10
1 IE 10
1 OE 10
1 IE 10
Farmer
Cancel
Risk
NT
NT
NT
NT
49E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-12
84E 12
7 BE 13
NT
NT
NT
NT
NT
NT
54E-12
83E-13
NT
NT
4 1E-13
NT
55E-10
NT
NT
1 2E 11
38E 11
1 OE 11
1 9E 11
1 2E 11
1 4E 11
69E 12
99E 12
1 9E tl
26E 10
1 6E 10
1 5E 10
1 7E 10
                                                                                                                                                 Adult      Child    School-age   Faimct
                                                                                                                                               Noncancei Noncancer Noncancer  Noncancer
                                                                                                                                                  HQ        HQ       HQ        HQ
NT
1 OE-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-06
1 9E-08
NT
96E 10
1 9E-08
NT
83E-09
NT
1 9E-08
NT
54E-07
24E-08
56E 07
40E09
1 OE-08
NT
4 6E-09
33E-07
NT
1 3E-07
58E-09
NT
1 2E-07
NT
2 OE 08
29E-10
NT
NT
NT
NT
NT
NT
IIT
NT
ra
nr
tit
NT
rn
NT
3 BE 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
44E 06
72E^)8
NT
36E09
72E-08
NT
3 IE 08
NT
72E4)8
NT
20E 06
89E08
2 1E-06
1 5E^)8
38E48
NT
1 7E 08
1 2E 06
NT
4 BE 07
2 2E 08
NT
4 4E 07
NT
75E 08
1 IE 09
NT
NT
NT
NT
NT
in
NT
m
NT
tIT
in
nr
nr
NT
23E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 7E 06
4 4E 08
NT
2 2E 09
44E 08
NT
1 9E 08
NT
44E-08
NT
1 2E 06
5 4E 08
1 3E 06
9 IE 09
2 3E 08
NT
10E 08
7 4E 07
NT
29E 07
1 3E 08
NT
2 7E-07
NT
45E 08
65E 10
NT
NT
NT
NT
HT
NT
NT
(IT
HT
NT
in
NT
Nl
NT
1 OE 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-06
1 9E 08
NT
96E 10
1 9E-08
NT
83E 09
NT
1 9E 08
NT
54E 07
24E 08
56E 07
40E 09
1 OE 08
NT
46E 09
3 3E 07
NT
1 3E 07
5 8E-09
NT
1 2E 07
NT
20E 08
29E 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HT
NT
NT
 jiume V Appendix V 14
-------
TABLE 11  Average ln>x   Jn Risks and Noncancer HQs in Subaiea W7
CHEMICAL
1. 2.3.7.8.9 HxCDF
1. 2.3.4.6,7.8 HpCDF
1.2.3,4.7.8.9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivalen!)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
rhaDlum
•Inc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
^articulate matter
^espirable particulates
Inhalation
Slope
Factor
(mg/kg-d)«-1
1 5E»04
1 5E+03
1 5E+03
t 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
OS4
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02825
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E-05
36E-05
13E-03
1 3E44
1 3E-03
25E-01
NA
NA
2 IE-OS
50E03
1 3E-03
1 3E^)3
18E-05
7 5E-02
5 OE-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E 09
1 89E-08
428E-08
24E-04
4 2E-06
37E-05
15E-04
336-08
16E05
7 1E-07
7 1E-07
94E-OS
43E-05
1 4E-03
50E-06
47E-04
1 5E-05
34E05
1 2E-04
32E-02
24E»00
9 1E-02
72E-02
7 2E-02
Subarea
W2 avg
W2avg
W2avg
W2avg

W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2avg
W2 avg
W2avg
Off site
Vapor
Cone
(ug/m3)
28E-11
89E-10
1 2E-10
1 BE -09
4 1E-09
23E-05
40E-07
36E-06
1 4E-05
32E-O9
1 SE-06
6 BE 08
8 BE -08
90E-06
4 IE 06
1 3E-04
48E-07
45E-05
1 4E-06
33E-06
1 2E-05
31E-03
23E-01
87E-03
69E-03
69E-03
Cancer
Adult
Dose
(mg/kg-d)
99E-16
31E-14
4 IE 15
64E-14
1 4E-13
81E-10
1 4E-11
1 3E-10
51E-10
1 1E-13
54E-11
24E-12
24E 12
32E-10
1 5E-10
47E-09
1 7E-11
16E-09
51E-11
1 1E-10
41E-10
1 1E-07
82E-06
31E-07
24E^>7
24E-07
Cancer
Child
Dose
(mg/kg-d)
25E-15
78E-14
1 OE-14
1 6E-13
36E-13
20E-09
35E-11
31E-10
1 3E-09
28E-13
1 3E 10
60E-12
60E-12
79E-10
36E-10
1 2E-08
42E-11
40E-09
1 3E-10
29E-10
1 OE-09
27E-07
20E-05
7 7E-07
6 1E-07
6 1E-07
Cancer
School-age
Dose
(mg/kg-d)
1 5E-15
47E-14
62E-15
96E 14
22E-13
1 2E-09
21E-11
1 9E-10
76E-10
1 7E-13
81E-11
36E12
36E-12
4 8E-10
22E-10
7.1E-09
25E-11
24E-09
76E-11
1 7E-10
61E-10
1 6E-07
12E-OS
4 6E-07
3 7E-07
37E-07
Cancer
Farmer
Dose
(mg/kg-d)
22E-15
7 OE-14
92E-15
14E-13
32E-13
18E-09
32E-11
28E-10
1 1E-09
25E-13
1 2E-10
53E-12
53E-12
71E-10
32E-10
1 1E-08
38E-11
35E-09
1 1E-10
26E-10
90E-10
24E4)7
1BE-OS
68E07
54E-07
54E-07
Noncancer
Adult
Dose
(mg/kg-d)
7 7E-15
24E-13
32E 14
50E-13
1 1E-12
63E-09
1 1E-10
97E-10
39E-09
87E-13
42E-10
19E-11
19E-11
25E-09
ME 09
37E-08
1 3E-10
1 2E-OB
39E-10
89E-10
32E-09
84E-07
64E-OS
24E-06
19E-06
19E-06
Noncancer
Child
Dose
(mg/kg-d)
2 9E-14
91E-13
1 2E-13
19E-12
42E-12
24E-OB
4 1E-10
36E09
1 5E-OB
32E-12
16E-09
70E-11
70E-11
92E-09
42E-09
14E-07
49E-10
46E-08
15E-09
33E-09
12E-08
3 IE-OS
24E-04
89E-06
7 IE 06
71E-06
Noncancer
School-age
Dose
(mg/kg-d)
1 7E-14
55E-13
72E-14
1 1E-12
25E-12
1 4E-OB
2 5E-10
2 2E-09
89E-09
20E-12
9SE-10
42E-11
42E-11
56E-09
26E-09
83E-OB
30E-10
2 BE -08
8 9E-10
2 OE-09
71E-09
19E-06
1 4E-04
54E08
43E-06
43E-06
Noncancer
Farmer
Dose
(mg/kgd)
7 7E-15
24E-13
32E-14
50E 13
1 1E-12
63E-09
1 1E-10
97E-10
39E-09
87E-13
42E-10
19E-11
19E-11
25E4W
1 1E-09
3 7E-OB
1 3E-10
1 2E-08
39E 10
89E 10
32E-09
ME^)7
64E-05
24E-06
19E-06
19E-06
 JOTES:
  NA - Not applicable
  NF-Not found
  NT - No toxiclty information
  HO - Hazard quotient
  HI - Hazard Index
 olumeV, Appendix V-14
-------
TABLE 1 i  Aveoge Inhalation Rir>ks and Noncancet HQs in Subaiea W2
CHEMICAL
1 2.3,789 HxCDF
1 2.3.4.6.78 HpCDF
1.2.3.4, 7.8,9 HpCDF
DCDF
Dioxm TEQ
Mumlnum
kntimony
vrsenlc
larium
Jen/Ilium
Cadmium
:hromium (h«xavalent)
.hromium (Invalent)
:opper
ead
ler-ury (and ItoHg)
lickei
•Ionium
ilvet
hallium
,nc
ydrogen chloride
otal mbogen oxides (NOx)
otal sulfur oxidus (SOx)
articulate matter
•spirabla participates

Inhalation
Slope
Factor
(mg/kg d)*-1
1 5E«04
1 5E«03
1 5E+03
1 5E»02

NA
NA
SO
NA
64
6 t
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF

RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
OOOOO61
02625
000175
NA
NA
NA
NF

Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
1 OE 04
75E OS
36E 05
1 3E 03
1 3E 04
1 3E 03
2 5E-01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E 03
1 BE 05
75E 02
50E 04
NA
NA
•NA
NF

Emission
Rate
 Not applicable
 NF = Not found
 NT = No loxicrty Information
 HQ * Hazard quotient
 HI  » Hazard Index
  iume v/ Appendix V-14
-------
TABLE 12  Average i\
                       jn Risks and Noncanccf HQs in Subarea W3
CHEMICAL
Acenaphlhene
Aeenaphttiylene
Acetaldehyde
Acetone
Acelophenone
Acrytonttrile
Anthracene
Benzene
Benzole icld
Benzofrlchlortde
Berco(a)anlhracene
Benzo(a)pytene
Berwo(b)fluoranlh*ne
Benzo(g.h,f)perytene
Benzo(k)fluoranthene
Bls(2-chloroethoxy) methane
Bls(2-chloroelhyl)ether
Bls(2 -enter olsopropy1)ether
Bls(2-ethylhexyl)phth8late
Bromodichtorotnethane
Bromoforrn
Bromomethane
Bromodlphenyl ether, p-
Butarwe. 2- (Methyl ethyl ketone)
Butylbenzylphthalate
Carbon dlsulfide
Carbon tetrachlorlde
Chlordane
Chk>ro-3-methylphenol, 4-
Chloroanlltne. p- (4-Chioroanllrne)
Chlorobenzene
Chlorobenzllale
Chloroethane (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthilene. beta
Chlorophenol, 2*
Chlorodiphenyl ether. 4-
Chrysene
Cresot, m-
Cresol. o- (2-Methylphenol)
Cresol p-
Crotonaldehyde
Cumone
DDE. 4,4'-
Dibenz(a ,h)anthracene
Dibromochloromethane
Dichlorobenzene. 1.3-
Dichlorobenzene, 1 .4-
Dichlorobenzene, 1,2-
Dichlofobenzidrne, 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)A-
NA
NF
7 7E-03
NA
NA
2 4E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
5 3E-02
1 3E+00
NF
NA
NA
2 7E-01
NA
8 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA -
NA
NA
RAC
1 (mg/m3)
00525
NF
000225
00675
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
0 04375
0 04375
0 004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
6 4E-04
2 5E-02
2 5E-02
1 4E-04
7 5E-02
4 3E-04
10E»00
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E-03
50E-03
5 OE-03
36E-04
NA
7 1E-02
50E-02
7 IE 04
1 4E-04
15E-05
NF
1 OE-03
1 4E-03
5 OE-03
7 1E-01
2 5E-03
NA
20E-02
1 3E-03
NF
NA
1 3E 02
1 3E-02
1 3E-03
NA
6 4E-04
NA
NA
5 OE-03
NA
57E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E-06
67E-06
3 OE-04
2 9E 03
29E-04
2 OE-04
55E-06
15E-05
, 1 IE-OS
32E-05
55E-06
55E-06
55E-06
55E-08
55E-08
67E-06
1 3E-05
67E-06
37E-05
IDE -04
55E-06
49E-04
67E46
5 IE-OS
55E-06
89E05
16E-04
55E-07
67E-08
67E-06
55E-06
37E-05
49E-04
27E-04
25E-04
67E-06
55E-06
67E-06
55E-06
55E06
55E-OS
55E 06
1 4E-04
55E-06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E-08
Subarea
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
WSavg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
Off-site
Vapor
Cone
(ug/m3)
29E 07
2 9E 07
1 3E 05
1 3E 04
1 3F.-05
69E-06
2 4E-07
6 5E-07
5 OE-07
14E-08
2 4E-07
2 4E-07
2 4E-07
2 4E-07
24E-07
29E-07
5 9E-07
2 9E 07
16E-06
45E-08
2 4E-07
22E-05
2 9E-07
23E06
2 4E-07
39E-08
70E-06
24E-OC
2 9E-07
2 9E-07
2 4E-07
16E-06
22E-05
12E-05
1 1E-05
2 9E-07
2 4E-07
2 9E-07
2 4E 07
2 4E 07
2 4E 07
24E 07
6 IE 06
24E 07
24E 08
2 4E-07
1 2E 06
24E 07
24E 07
24E 07
1 5E 06
2 IE 09
Cancer
Adult
Dose
(mg/kg-d)
1 OE-11
1 OE-11
4 7E-10
45E-09
45E-10
31E-10
85E-12
23E-11
1 BE 11
5 OE-11
85E-12
65E-12
85E-12
85E-12
85E-12
1 OE-11
2 1E-11
1 OE-11
S8E-11
1 6E-10
85E-12
76E-10
1 OE-11
8 OE-11
BSE 12
1 4E-10
25E-10
85E-13
1 OE-11
1 OE-11
85E-12
57E-11
76E-10
41E-10
38E-10
1 OE-11
85E-12
10E 11
85E-12
85E-12
85E-12
85E 12
22E-10
85E 12
85E 13
BSE 12
4 1E-11
BSE 12
85E-I2
BSE 12
52E 11
73E-14
Cancer
Child !
Dose
(mg/kg-d)
26E-11
26E 11
1 2E-09
1 IE-OS
1 1E-09
78E-10
2 IE-It
57E-11
44E-11
1 2E-10
21E-11
2 1E-11
2 1E-11
21E-11
2 1E-11
26E-11
51E-11
26E-11
1 4E-10
40E-10
21E-11
19E-09
26E-11
20E-10
2 1E-11
3 4E-10
61E-10
2 1E-12
26E-11
26E-11
21E-11
1 4E-10
19E-09
IDE -09
95E-10
26E-11
21E-11
26E-11
21E-11
21E-11
2 1E-11
2 IE 11
54E 10
2 IE 11
2 IE 12
2 IE 11
1 OE 10
2 IE 11
2 IE 11
2 IE II
1 3E 10
1 BE 13
Cancer
School-age
Dose
(mg/kg-d)
16E-11
1 6E-11
70E-10
6 8E 09
68E 10
47E-10
1 3E-11
34E-11
26E-11
75E-11
13E-11
1 3E-11
13E-11
1 3E-1 1
13E-11
16E-11
31E-11
16E-11
87E-11
24E-10
1 3E-11
1 1E-09
16E-11
12E-10
13E-11
21E-10
37E-10
1 3E-12
16E-11
16E-11
1 3E-11
86E-11
1 1E-09
62E-10
57E-10
16E-11
13E-11
16E-11
1 3E-11
1 3E-11
1 3E-11
1 3E-11
32E-10
13E-11
1 3E 12
1 3E-11
6 IE 11
1 3E 11
1 3E-11
1 3E 11
7 BE 11
1 IE 13
Cancer
Farmer
Dose
(mg/kg-d)
23E-11
23E-11
1 OE-09
1 OE-08
1 OE-09
70E-10
1 9E-11
51E-11
39E-11
1 1E-10
19E-11
1 9E-11
19E-11
19E-11
19E-11
23E-11
46E-11
23E-11
1 3E-10
36E-10
19E-11
1 7E-09
23E-11
1 BE-10
19E-11
3 IE 10
S4E-10
1 9E-12
23E-1t
23E-11
19E-11
1 3E-10
17E-09
92E-10
84E 10
23E-11
19E-11
23E-11
19E-11
19E-11
19E-11
:19E-11
48E-10
1 9E-11
19E-12
1 9E-11
9 IE 11
1 9E-11
1 9E-11
1 9E-11
1 IE 10
1 6E 13
Noncancer 1
Adult
Dose
(mg/kg-d)
81E-11
81E-11
3 6E-09
3 5E-08
35E-09
24E-09
66E-11
1 8E-10
1 4E-10
39E-10
66E-11
66E-11
66E-11
66E-11
66E-11
81E-11
1 6E-10
81E-11
4 5E-10
12E-09
66E-11
59E-09
B1E-11
62E-10
66E-11
1 1E-09
19E-09
66E-12
8 IE 11
81E-11
66E-11
44E-10
S9E09
32E09
3 OE-09
8 IE-It
66E-11
81E-11
66E-11
66E 11
66E-11
66E-11
1 7E 09
66E-11
66E 12
66E 11
32E-10
66E 11
66E 11
66E 11
40E 10
56E 13
vloncancet 1
Child J
Dose
(mg/kg-d)
30E-10
30E-10
1 4E-08
1 3E-07
1 3E-08
9 1E-09
2SE-10
66E-10
51E-10
14E-09
25E-10
2 5E-10
25E-10
25E-10
25E-10
30E-10
60E-10
30E-10
17E-09
46E-09
25E-10
2 2E-08
30E 10
23E-09
2 5E-10
40E-O9
71E-09
25E-11
30E-10
30E-10
25E-10
1 7E-09
22E-08
12E08
1 1E-08
30E-10
25E-10
30E-10
25E 10
25E-10
25E-10
25E 10
63E09
25E 10
25E 11
25E 10
1 2E 09
25E 10
25E 10
25E 10
1 5E 09
2 IE 12
sloncancer f
School age
Dose
(mg/kgd)
1 8E-10
1 8E-10
8 2E 09
7 9E 08
8 OE-09
5 5E-09
1 5E-10
40E-10
3 IE 10
87E-10
1 5E-10
1 5E-10
1 5E-10
1 5E-10
1 5E-10
1 8E-10
36E-10
1 8E-10
1 OE-09
2 BE -09
1 5E 10
13E^)8
1 8E-10
1 4E 09
1 5E-10
24E09
4 3E-09
15E-11
1 8E-10
1 8E-10
1 5E 10
1 OE-09
1 3E-08
7 2E-09
6 7E-09
1 8E-10
1 5E-10
1 8E-10
1 5E 10
1 5E-10
1 5E-10
1 5E-10
3 BE 09
1 5E 10
1 5E-11
1 5E 10
72E 10
1 5E 10
15E 10
1 5E 10
9 1E 10
1 3E 12
vloncancer
Farmer
Dose
(mg/kg-d)
81E-11
81E-11
36EOT
3 5E-08
3SE09
24E-09
66E-11
1 8E-10
1 4E-10
39E 10
66E 11
66E-11
66E-11
66E-11
66E-11
81E-11
1 6E-10
81E-11
45E-10
12E-09
66E-11
59E-09
81E-11
62E-10
66E11
1 1E-09
19E-09
66E-12
81E-11
8 IE-It
66E-11
44E 10
59E-09
32E09
3 OE-09
8 IE-It
66E 11
8 IE 11
66E 11
66E-11
66E-11
66E 11
1 7E 09
66E-11
66E 12
66E 11
32E 10
66E 11
66E 11
66E 11
40E 10
56E 13
 /olume V. Appendix V-14
-------
TARI E  1?  Average Inhalation Ri'.ks and Noncancpt MQs in Subaroa W3
CHEMICAL
Nitroanilme, 4-
Nrtfobenzan*
Nitrophenol. 2-
Mrtiophenol. 4-
M Nrtroso-dl-n butylamine
H Nitroso-dl-n-propytamine
N-Nrtrosodiph«ny1amine (Diphenylamine)
Monachlorobiphenyt
Octachlofobiphanyl
3«ntachlorob«nz*n«
^entachlofobiphenyl
'entachloronltroberuene
3entachlofoph»nol
'henanthr«ne
tienol
'ytene
>aliol* (5-(2-Piopeny1)-1 .3 benzodioxoie)
>tyten«
"etrachloroblphenyt
•ttachloroethane. 1.1.1.2-
Mj»chloioethan». 1.1.2.2-
»bichloioettien«
e(rachloroph«nol. 2.3.4,6-
oluene
MchkHO-1.2,2-lirfluoto«than«. 1.1.2-
fichlorobervfene. 1.2.4-
rlchlofoblphenyl
richloioettian*. 1,1,1- (Methyl chloroform)
richkxocthan*. 1.1,2-
rlchloro«(hene
richtorofluoromethan*
richlorophenol. 2.4.5-
iichkxophanol. 2,4,6-
inyl acetate
Inyl chloride
ylena, m/p- (m/p-Dlmethyl benzene)
yl«n«. o- (o-Dim«1hy1 benzene)
V
3.7.8-TCDD
2.3,7.8 PCDD
234.78 HxC DO
2 3.6 7.8 HxCDD
2 3789H*CDD
2.3,4,6. 7.8-HpCDD
CDD
3,78-TCDF
23 7,8 PCDF
3,4 7,8 PCDF
2,34 7.8HxCDF
23678 H»CDF
3,46.7 8H«CDF
nhalation
Slope
Factot
(mg/kg d)A-1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
60E 03
NA
NA
1 OE-02
NA
30E01
NA
NA

1 5E»05
75E+04
5E»04
5E+04
5E»04
5E»03
5E»02
5E«04
5E»03
5E*04
5Et04
5E*04
5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
002625
NA
0525
0 02825
NF
025
NA
0 02625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E-04
75E-03
NA
1 5E-01
75E-03
NF
7 1E 02
NA
7 5E 03
NA
25E 03
75E 03
29E 02
2 1E»00
1 4E 02
NA
7 1E 02
1 OE 03
NA
50E 02
2 5E 02
NA
1 4E-02
NA
50E-01
50E-01

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(U'sec)
67E 06
55E06
6 7E 06
55E 06
1 2E 04
67E-06
6 7E46
1 4E-08
,1 4E-08
48E 05
1 4E-08
34E-05
55E-06
67E-06
55E-06
55E-06
1 2E 04
23E-05
1 4E-08
55E-06
55E^)6
5 1E^>5
6 BE 06
61E^)4
33E^)4
55E 06
30E08
1 3E4K
1 3E-05
1 9E 05
2 5E 04
55E06
55E 06
64E 05
2 5E-04
3 BE 04
55E06

1 08E 11
6 78E-11
895E 11
1 66E 10
1 09E-10
1 24E 09
6 15E 09
8 77E 11
3 4SE 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
\rV3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3tvg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg

W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3 avg
W3 avg
W3avg
Off site
Vapor
Cone
(ug/m3)
29E 07
24E-07
29E 07
24E 07
53E 06
2 9E 07
29E 07
62E 10
82E-10
2 1E-06
62E-10
15E-06
2 4E-07
2 9E 07
24E^)7
24E^)7
5 IE 06
99E 07
62E-10
2 4E 07
2 4E 07
23E06
30E 07
27E05
1 5E OS
24E 07
1 3E 09
55E-07
55E^)7
82E-07
1 IE 05
2 4E 07
24E 07
2 8E 06
1 IE 05
1 7E 05
2 4E 07

48E 13
30E 12
39E 12
73E 12
48E 12
55E 11
2 7E 10
39E 12
1 5E 11
2 IE 11
63E 11
59E It
66E 11
Cancer
Adult
Dose
(mg/kg-d)
1 OE 11
85E-12
1 OE 11
85E 12
1 9E-10
1 OE-11
1 OE-11
22E 14
22E-14
74E 11
22E 14
52E-11
85E-12
1 OE-11
85E-12
85E-12
1 8E-10
35E-11
22E-14
85E-12
BSE 12
79E-11
1 1E-11
95E 10
5 IE 10
85E 12
4 7E 14
1 9E-11
1 9E 11
29E-11
3 BE 10
85E 12
85E 12
1 OE 10
3 BE 10
59E-10
85E 12

1 7E 17
1 IE 16
1 4E 16
2 BE 16
1 7E 16
1 9E 15
95E 15
1 4E 16
53E 16
7 2E 16
22E 15
2 1E 15
23E 15
Cancer
Child
Dose
(mg/kg d)
26E-11
2 1E-11
26E 11
2 IE 11
47E-10
26E 11
26E-11
54E-14
54E-14
18E-10
54E 14
1 3E-10
2 1E-11
26E-11
21E-11
2 IE 11
44E-10
87E-11
54E-14
2 IE-It
2 IE 11
20E 10
26E 11
24E 09
1 3E 09
2 IE 11
1 2E 13
48E-11
48E-11
72E-11
95E-10
2 1E-11
2 IE 11
25E-10
95E-10
15E-09
2 1E-11

42E 17
26E 16
35E 16
64E 16
42E 16
A BE 15
24E 14
34E 16
1 3E 15
1 BE 15
55E 15
52E 15
58E 15
Cancer
School age
Oos«
(mg/kgd)
1 6E 11
1 3E-I1
1 6E-11
1 3E-11
28E 10
1 6E-11
1 6E-11
33E 14
33E-14
1 IE 10
33E-14
79E-11
1 3E-11
16E-11
1 3E-11
1 3E-11
27E-10
52E 11
33E-14
1 3E-11
1 3E-11
1 2E 10
1 6E-11
1 4E 09
77E-10
1 3E-11
70E 14
29E 11
29E 11
43E-11
57E-10
1 3E-11
1 3E 11
1 5E-10
57E-10
69E 10
1 3E 11

25E 17
1 6E 16
2 IE 16
39E 16
2 5E 16
29E 15
1 4E 14
2 OE 16
60E (6
1 IE 15
3 3E 15
3 IE 15
3SF !S
Cancer
Farmer
Dose
(mg/kgd)
23E-11
19E-11
23E 11
1 9E-11
42E 10
23E-11
23E-11
48E-14
48E-14
1 6E-10
48E-14
1 2E-10
19E-11
23E 11
19E-11
19E-11
40E-10
77E-11
48E 14
19E-11
19E-11
1 8E-10
23E 11
21E-09
1 1E-09
19E-11
10E-13
43E 11
43E-H
64E 11
84E-10
19E-11
1 9E-11
22E-10
84E-10
1 3E-09
1 9E-11

37E 17
23E 16
3 IE 16
57E 16
37E 16
43E 15
2 1E 14
30E 16
1 2E 15
t 6E 15
49E 15
461- 15
s?r 15
Noncancer
Adult
Dose
(mg/kg d)
8 1E-11
66E 11
8 1E-11
66E-11
1 5E-09
8 IE 11
8 1E-11
1 7E-13
1 7E 13
57E-10
1 7E-13
4 1E-10
66E 11
81E-11
66E-11
66E-11
1 4E 09
27E-10
1 7E-13
66E-11
66E-11
62E-10
82E 11
74E09
40E-09
66E-11
36E 13
1 5E-10
1 5E 10
22E 10
3 OE 09
66E 11
66E-11
77E 10
30E 09
4 6E 09
66E 11

1 3E 16
82E 16
1 IE 15
20E 15
1 3E 15
1 5E 14
74E 14
1 IE 15
42E 15
56E 15
1 7E 14
1 BE 14
i nr 14
Noncancer
Child
Dose
(mg/kg-d)
30E 10
25E-10
30E-IO
25E-10
54E-09
30E-10
30E 10
63E-13
63E 13
21E-09
63E 13
15E-09
25E-10
30E-10
25E-10
25E-10
52E-09
10E09
63E-13
25E-10
25E-10
23E4»
31E-10
2 BE 08
1 5E-08
25E-10
1 4E 12
56E 10
56E 10
84E 10
1 IE 08
25E 10
25E 10
29E09
t IE 08
1 7E 08
25E 10

49E 16
3 IE 15
40E 15
75E 15
49E 15
50E 14
7 8F 13
39F 15
1 6t 1 4
? 1C 14
fi 4F 14
6 OF 14
fiBF 14
Noncancer
School-age
Dose
(mg/kg-d)
1 BE-10
15E 10
1 8E-10
1 5E-10
33E-09
1 8E-10
1 8E-10
38E-13
38E-13
1 3E-09
38E-13
92E-10
1 5E-10
1 8E-10
15E-10
1 5E-10
31E-09
61E-10
38E-13
1 5E-10
1 5E-10
1 4E-09
1 9E 10
1 7E 08
90E-O9
1 5E 10
82E 13
34E 10
34E 10
5 IE 10
67E 09
1 5E-10
1 5E 10
1 7E 09
67E09
1 OE 08
1 5E 10

29E 16
1 8E 15
24E 15
45E 15
30E 15
34E 14
1 7E 13
24E 15
94E 15
1 3E 14
39E 14
3 BE 14
4 1E 14
Noncancer
Farmer
Dose
(mg/kg d)
B1E 11
66E-11
8 IE 11
66E-11
1 5E 09
8 IE 11
8 IE 11
1 7E 13
1 7E-13
57E-10
1 7E-13
4 1E-10
66E-11
8 IE 11
66E-I1
66E-11
1 4E^)9
2 7E-10
1 7E-13
66E 11
66E-11
62E-10
82E 11
74E09
40E-09
66E-11
36E-13
1 5E-10
1 5E-10
22E-10
30E09
66E-11
66E 11
77E-IO
30E09
46E09
66E 11

1 3E 16
82E 16
1 IE 15
20E 15
13E 15
1 5E 14
74E 14
1 1E 15
42E 15
56E 15
1 7E 14
1 BE 14
1 8F 14
  rlume V, Appendix V 14
-------
TABLE 12  Average Inhalation Risks and Noncancel HQs in Subarea W3
ZHEMICAL (
Dtchlorodifluoromerhane
9ichloro«ttiane, 1.1- (Ethyhdene dichlorlde)
Dichloroelhane. 1,2-
Dlchloroethena. 1,1- (Vinylidme chloride)
Dichloroethene (bans). 1 ,2-
Oichlorophenol,2.4-
Dkhloropropane. 1.2- (Propylene dichloride)
Dtchloroptop«n« (cis), 1.3-
atchloropropene (trans), 1 ,3-
Dfethylphlhalato
DimethoxybenrWIn*. 3.3'-
Oimethytphvnol, 2.4-
LHmetnyrphthalate
> n butylphthalate
Dinitrotoluen*. 2.6-
3inHro-2-melhy1ph«nol. 4.6-
Dinlbophenol. 2,4-
Drnltrotoluene. 2.4-
Dtoxana. 1 .4-
3i(n)octyl phttialale
3. 2,4-
ithyl mettiacrylate
£ thyl benzene
zthyiene dibromide
Ethylene oxld«
ithylene thlouraa
rluoranth*ne
"luorene
rormaldehyde
"urfural
-(•ptachhx
Heptachlorobtphenyl
-toxachlorobenzena
Haxachloroblphanyl
lexachlorobutadiene
-laxachlorocyclohaxana, gamma (Lindana)
(exachlorocyclopentadiene
lexachtoroethane
Hexachlorophene
-taxation*, 2-
ndeno(1 ,2,3-cd)pyrana
sophorona
vlaleic hydrazida
vlethoxychlof
Uettiyl-t-butyl athar
Uethyl-2-P»ntanone. 4- (MIBK)
^ethylene chlorida
\Aethylnaphthalene. 2-
Monochlorobiphenyt
Naphthalene
'Jittoaniline 2-
^rtroamline. 3-
Inhalahon
Slope
Factor
mg/kg-d)*- 1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E-01
35E-01
NA
NA
NA
45EXI2
NA
45E+00
NA
1 6E*00
NA
7 BE -02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0 004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E 02
36E-02
NA
23E4)3
5 OE-03
75E-04
2 9E-04
1 4E-03
1 4E-03
20E-01
NA
5 OE-03
NA
2 5E-02
25E-04
NF
5 OE-04
50E-04
NA
50EX)3
2 5E-03
2 3E-02
7 IE 02
1 4E-05
NA
20E 05
1 OE-02
1 OE-02
50E 02
36E 03
1 3E 04
NA
2 OE-04
NA
50E05
75E-05
SOE06
25E04
75E-05
NF
NA
5 OE 02
1 3E 01
1 3E 03
2 1E 01
5 7E 03
2 IE 01
NF
HA
1 OE 02
1 4E 05
NF
Emission
Rate
(g/see)
2 5E 04
3E 05
3E 05
3E-05
3E-05
55E-06
3E-05
3E 05
3E-05
1 7E-05
1 2E-04
55E-06
5SE-06
1 6E-05
55E-06
55E-06
55E06
55E-06
49E-04
55E08
39E-05
2 5E 04
5 OE-04
1 2E-04
3 IE 05
1 5E-10
55E 06
87E-06
6 IE 04
55E06
5 5E-07
1 4E-08
55E06
1 4E-08
1 OE 04
55E-05
55E 06
55E06
32E 05
6 4E-05
55E 06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3 avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
Off site
Vapor
Cone
(ug/m3)
1 IE 05
55E 07
55E 07
5 5E 07
5 5E-07
24E-07
5 5E-07
5 5E-07
5 5E-07
7 4E-07
51E-06
2 4E-07
2 4E-07
6 9E-07
2 4E-07
2 4E-07
2 4E-07
2 4E-07
2 2E 05
2 4E-07
1 7E 06
1 IE 05
22E-05
51E-06
1 3E-06
64E-12
2 4E-07
2 9E 07
2 7E-05
2 4E-07
2 4E 08
62E-10
2 4E 07
62E 10
4 4E-06
24E 06
2 4E 07
2 4E-07
1 4E 06
28E06
24E 07
29E 07
5 IE 06
2 4E 08
55E 07
55E 07
1 7E 05
1 BE 06
7 3E 10
2 4E 07
29E 07
29E 07
Cancer
Adult
Dose
(mg/kg-d)
38E-10
19E-11
1 9E 11
19E-11
1 9E-11
85E-12
1 9E-11
19E-11
19E-11
26E-11
1 8E-10
85E-12
85E-12
24E-11
85E-12
B5E-12
85E-12
85E-12
77E-10
85E-12
60E-11
38E-10
77E-10
1 8E-10
47E-11
23E-16
85E-12
10E-11
94E-10
BSE 12
85E-13
22E-14
85E-12
22E-14
1 6E-10
85E-11
85E-12
85E-12
50E-11
1 OE 10
85E 12
10E 11
1 BE 10
85E 13
1 9E 11
1 9E 11
6 IE 10
65E 11
26E 14
BSE 12
1 OE 11
1 OE 11
Cancer
Child
Dose
(mg/Vg-d)
95E-10
4BE-11
48E-11
4BE-11
48E-11
2 1E-11
48E-11
4BE-11
48E-11
65E-11
44E-10
2 1E-11
2 IE-It
80E-11
2 1E-11
2 1E-11
2 1E-11
2 1E-11
19E-09
2 1E-11
1 5E 10
95E-10
t 9E-09
44E-10
1 2E-10
56E-16
2 1E-11
26E-11
23E-09
2 1E-11
21E-12
54E-14
21E-11
54E-14
39E-10
2 1E-IO
2 1E-11
2 1E-11
1 2E-10
25E-10
2 IE 11
26E 11
44E 10
2 IE 12
4 BE 11
48E 11
1 5E 09
1 6E 10
6 4£ 14
2 IE 11
2 6E 11
2 HE 11
Cancer
School-age
Dose
(mg'kg-d)
57E-10
29E-11
29E 11
29E 11
29E-11
1 3E-11
29E-11
29E 11
29E-11
39E-11
2 7E-10
3E-11
3E-t1
7E-11
3E-11
3E-11
3E-11
3E-11
2E-09
3E 11
90E-11
57E-10
12E49
2 7E-10
7 1E-11
34E 16
13E-11
1 6E-11
1 4E-09
1 3E-11
1 3E-12
33E-14
13E-11
33E-14
24E-10
1 3E-IO
1 3E-11
1 3E-11
75E 11
1 5E-10
1 3E 11
16E 11
27E-10
1 3E 12
29E It
2 9E 11
92E 10
9 7E 11
39E 14
1 3E 11
1 6E 11
1 6E 11
Cancer
Farmer
Dose
(mg/kg-d)
84E-10
43E-11
43E 11
43E 11
43E 11
1 9E-11
43E-11
43E 11
43E 11
58E-11
40E-10
1 9E-11
19E-11
54E-11
19E-11
19E-11
19E-11
19E-11
1 7E-09
1 9E 11
1 3E 10
84E-10
I7E-09
40E-10
1 1E-10
50E-16
19E-11
23E-11
21E-09
19E 11
1 9E-12
48E-14
19E-11
4BE-14
35E-10
1 9E 10
1 9E-11
1 9E-11
1 1E-10
22E-10
1 9E-11
23E-11
40E 10
1 9E 12
4 3E 11
4 3E 1 1 "
1 4E 09
1 4E 10
5 7E 14
1 9C 11
2 3E 11
2 If 11
Noncancer
Adult
Dose
(mg/Vg-d)
3 OE 09
1 5E-10
15E-10
1 5E-10
1 5E-10
66E-11
1 5E-10
1 5E-10
1 5E-10
20E-10
14E-09
66E-11
66E-11
1 9E-10
66E-11
66E-11
66E-11
66E-11
60E-09
66E-11
47E-10
30E-09
60E-09
14E-09
37E-10
1 BE 15
66E-11
8 IE 11
73E09
66E-11
66E-12
1 7E-13
66E-11
1 7E-13
1 2E-09
66E-JO
66E 11
66E-11
39E-10
77E 10
66E 11
81E-11
1 4E 09
66E 12
1 5E-10
1 5E 10
4 BE 09
50E 10
20E 13
66E 11
8 IE 11
8 IF 11
Noncancer
Child
Dose
(mg/kgd)
1 IE 08
56E 10
56E-10
56E-10
56E-10
25E-10
56E-10
56E-10
56E-10
76E-10
52E-09
25E-10
25E-10
70E-10
25E-10
25E-10
25E-10
25E-10
2 2E-08
25E-10
1 7E-09
1 1E-08
2 2E-08
S2E-09
1 4E-09
66E-15
25E-10
30E-10
2 7E 08
25E-10
25E-11
63E-13
25E-10
63E-13
45E09
2 5E-09
25E-10
25E-10
1 4E-09
29E-09
25E-10
30E 10
52E 09
25E 11
5 BE 10
56E 10
1 BE 08
1 9E 09
75E 13
25E 10
30E 10
3 or 10
\loncancer
School-age
Dose
(mg/kg-d)
67E-09
34E-10
34E-10
34E-10
34E-10
15E-10
34E-10
34E-10
34E-10
46E-10
31E-09
1 5E-10
1 5E-IO
43E-10
1 5E-10
1 5E-10
1 5E-10
1 5E-10
1 3E-08
15E-10
1 1E-09
67E09
14E-08
31Efl9
83E-10
40E-15
1 5E 10
1 BE 10
1 7E4)8
1 5E-10
1 5E-11
38E 13
15E 10
3 BE 13
27E^9
15E^»
1 5E-10
1 5E-10
8 7E-10
1 7E 09
1 5E 10
1 BE 10
3 1E 09
1 5E-11
34E 10
34E-10
1 1E 08
1 1E 09
45E 13
1 5E 10
1 BE 10
1 8E 10
Noncancer
Farmer
Dose
(mg/kgd)
3 OE-09
1 5E-10
1 5E-10
1 5E-10
1 5E-10
66E-11
1 5E-10
1 5E-10
1 5E-10
20E-10
ME -09
66E-11
66E-11
1 9E-10
66E-11
66E-H
66E-11
66E-11
6 OE-09
66E-11
47E-10
30E4>9
6 OE-09
1 4E-09
37E-10
18E-15
66E-11
8 IE 11
73E4»
66E-11
66E-12
1 7E-13
66E It
1 7E-13
t 2E-09
66E 10
66E 11
66E-11
39E 10
77E-10
86E 11
81E-11
1 4E-09
66E 12
1 5E 10
1 5E 10
4 BE 09
50E 10
20E 13
66E-11
8 1E 11
8 IF 11
/olume V. Appendix V 14
-------
TABLE 12  Average Inhalation Risks and Noncaneer MQs in Subarea W3
CHEMICAL
Dichlorodrfluoromethane
Dichloroethana, 1,1- (Elhylidene dichlonde)
Drchloroetnana. 1.2
Dichloroethena. 1,1- (Vinylidine chtonde)
Dichloroeltiena (trans). 1.2-
Qichlotophenol. 2.4-
Dichlotopiopane. 1 .2- (Propytene dichlortde)
Dichloroptopen* (els), 13
Dichloroprop«n« (trans), 1,3-
Diettiylphthalala
Olmethoxyfa«nzidin«. 3.3'-
Dim«thylph»nol, 2.4-
IHmrthylpnthalaU
Hi n butylphthalato
3lnrtjotolu«ne. 2.6-
Dintbo-2-methylphenol, 4,6-
3inttroph«nol. 2,4-
Jimtjotoluene 2.4-
}loxana. 1,4-
Ji(n)octyl phthalate
J. 2.4-
Ihyt methacrylale
ittiyl benzene
Ithylene dibromlde
Ihytana oxida
thylena thlouraa
luoranthena
luorena
ormaldehyde
urfural
(•ptachlor
fopfechlorobiphanyl
lexachlorobenzena
lexachloroblphenyl
l«xachloiobutadiene
lexachlorocyclohaxana, gamma (Lindane)
laxachlorocyclopentadiane
lexachlotoethane
lexachlorophene •;
lexanona. 2-
ideno(1 .2.3-cd)pyian«
ophorona
laleic hydruida
lethoxychlor
lethyl-t-butyl ether
lottiyl 2 Pentanone. 4- (MIBK)
Ibthytene chloride
ethylnaphthalene. 2-
lonc-chlorobiphenyl
aphthalene
rttoanilina. 2-
rtroanihne. 3-
Inhalation
Slope
Facloi
(mg/kg-d)"-1
MA
NA
9 IE 02
1 2E»00
NA
NA
NA
1 3E4)1
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E4>1
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E»00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
16E-03
NF
NA .
NA •
NA
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0 004375
075
002
075
NF
NA
0035
OOOOO5
NF
Inhalation
RfD
(mg/kg-d)
1 4E 02
36E 02
NA
23E 03
50E 03
75E 04
29E^4
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
25E 02
25E^>4
NF
50EO4
50E-04
NA
50E43
25E^)3
23E^)2
7 1E42
1 4E-05
NA
20E^5
1 OEO2
1 OE 02
50E-02
36E 03
1 3E-04
NA
20E44
NA
50E05
75E05
50E-06
2 5E-04
75E-05
NF
NA
50E02
1 3E-01
1 3E 03
2 1E-01
5 7E 03
2 1E-01
NF
HA
1 OE 02
1 4E-05
NF
Emission
Rate
(g/sec)
2 5E-04
1 3E 05
1 3E 05
1 3E 05
1 3E 05
55E 06
3E 05
3E-05
3E-05
7E 05
2E-04
55E-08
55E-06
16E 05
55E 06
55E-06
55E 06
55E 06
49E 04
55E 06
39E 05
25E 04
50E 04
1 2E 04
31E-05
15E-10
55E 06
67E4»
6 1E-04
55E-06
5 5E-07
1 4E-08
55E 06
1 4E-08
1 OE 04
5 5E-05
55E06
55E-06
3 2E 05
6 4E 05
55E06
6 7E 06
1 2E 04
55E-07
1 3E-05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
W3avg
W3avg
W3 avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3*vg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3ivg
W3avg
W3avg
W3avg
W3avg
VV3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
;W3avg
W3avg
W3avg
W3avg
W3avg
W3 avg
W3avg
W3avg
W3avg
W3 avg
W3 avg
Adult
Cancer
Risk
NT
NT
1 BE 12
23E-11
NT
NT
NT
25E 12
25E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 4E-10
1 7E-11
NT
NT
NT
42E-11
NT
38E-12
NT
14E-11
NT
12E-11
NT
NT
1 2E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 OE-12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
44E 12
58E -11
NT
NT
NT
62E 12
62E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
34E-10
41E-11
NT
NT
NT
1 1E-10
NT
96E-12
NT
34E-11
NT
30E-11
NT
NT
30E-13
NT
NT
NT
NT
NT
m
NT
HT
25E-12
NT
m
W
in
NT
School age
Cancer
Risk
NT
NT
2 7E 12
35E-11
NT
NT
NT
38E 12
38E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E-10
25E-11
NT
NT
NT
64E-11
NT
58E-12
NT
2 1E-11
NT
18E-11
NT
NT
1 8E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 5E 12
m
NT
NT
NT
tJT
Farmer
Cancer
Risk
NT
NT
39E 12
52E-11
NT
NT
NT
56E-I2
56E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E-10
37E-11
NT
NT
NT
94E-I1
NT
85E-12
NT
30E-11
NT
27E-11
NT
NT
27E-13
NT
NT
NT
NT
NT
NT
NT
NT
22F. 12
NT
NT
tIT
NT
in
                                                                                                                                              Adult      Child   School age  Farmer
                                                                                                                                           Noncaneer Noncaneer Noncaneer Noncaneer
                                                                                                                                              HQ       HQ        HQ        HQ
2 IE -07
4 2E-09
NT
6 7E-08
30E4)8
8 BE 08
5 3E 07
1 1E-07
1 1E-07
1 OE-09
NT
13E-08
NT
75E^)9
27E-07
NT
3E4>7
3E4>7
NT
3E-08
9E^)7
3E-07
84E4)8
97E-05
NT
88E-11
66E-09
8 IE 09
1 5E-07
1 9E48
53E-08
NT
33E-07
NT
24E-05
BSE 46
13E^5
2 7E 07
5 1E46
NT
NT
1 6E49
1 1E^)8
53E-09
70E 10
26E OB
2 2E-08
NT
NT
66E 09
S BE 06
NT
7 7E-07
1 6E-08
NT
2 5E-07
1 IE 07
3 3E-07
20E06
39E-07
39E-07
3 BE -09
NT
50E 08
NT
2 BE 08
99E-07
NT
50E-07
50E-07
NT
5 OE 08
70E07
49E-07
3 IE 07
36E04
NT
33E-10
2 5E-08
3 OE-08
55E-07
69E-08
20E-07
NT
1 2E-06
NT
9 IE 05
3 3E-05
50E-05
99E 07
1 9E-05
NT
NT
60E 09
4 IE 08
20E 08
26E 09
9 BE 08
B ir 08
NT
NT
2SE 08
2 1E 05
tIT
4 7E-07
95E-09
NT
1 5E-07
68E 08
20E 07
12E-06
2 4E 07
24E-07
23E-09
NT
3 OE-08
NT
1 7E-08
6 OE-07
NT
3 OE 07
3 OE-07
NT
3 OE-08
42E 07
3 OE-07
1 9E 07
2 2E-04
NT
20E-10
1 5E-OB
1 BE 08
33E-07
4 2E-08
1 2E-07
NT
75E-07
NT
5 5E 05
20E-05
30E-05
60E 07
1 2E-05
NT
NT
36E-09
25E 08
1 2E 08
1 6E 09
60E 08
5 OF. 08
NT
NT
1 SE 08
1 IF 05
NT
2 IE 07
42E-09
NT
6 7E-08
30E 08
8 BE 08
53E-07
1 IE 07
1 1E-07
1 OE-09
NT
1 3E-08
NT
75E09
2 7E-07
NT
3E-07
3E-07
NT
3E48
9E-07
3E07
8 4E 08
9 7E-05
NT
8 BE 11
66E 09
B IE 09
1 5E-07
1 9E 08
53E-OB
NT
33E-07
NT
2 4E 05
8 BE 06
1 3E-05
2 7E 07
5 IE 06
NT
NT
1 6E-09
1 IE 08
5 3E-09
70E-10
26E 08
? 2F 08
NT
NT
66E 09
56E 06
Ml
 >lume V. Appendix V-'A
-------
ABLE 12  Average Inhalation Risks and Noncancer HQs in Subarea W3
iHEMICAL
•litroaniline, 4-
jitrobenzene
Jitrophenol, 2-
litrophenol, 4-
J Nitroso-di n-butylamlne
J Nitroso-di-n-propylamine
J-NHrosodiphenylamine (Ophanylamina)
Jonachlorobiphenyl
JctachtoroWphenyl
'•ntachlorobenzene
'entochlorobiphenyl
>entcchlofonKrobenzene
'entachloropheno)
'henanthrene
'henol
'yrene
>afrole (5-(2-Propenyl)-1.3-benzodloxole)
ilyrene
[ etrachloroblphenyl
fetrachteroethane, 1,1,1.2-
retrachloroethane. 1.1.2,2-
r»tr senior oethene
atracMorophenol, 2.3,4,6
Toluene
•richk>ro-1.2,2-trifluoro«than«. 1.1.2-
rnchlorobenzena, 1,2,4-
richtoroblphenyl
frlchtoroettiane. 1.1.1- (Methyl chloroform)
frtchloroethane, 1,1,2-
rrichtor oethene
rrichlorofluoromethane
Frtchlorophenol. 2.4.5-
rrichlorophano). 2,4.6-
finyl acetate
/inyt chkxide
(ylana, m/p- (m/p-Dimerhyl benzene)
(ylene, o- (o-Dimettiyt benzene)
',3,7.8-TCDO
1.2.3,7,8-PCDD
1.2,3 4,7 8-HxCDO
1,2,3 8.7 8-HxCDD
1.2.3.7.8.9 HxCDD
l.2.3,4.6.7.8-HpCDD
3CDD
?.3.7.8-TCOF
1.2,3.7.8 PCDF
!.3.4.7.8-PCDF
l.2.3.4.7.8-HxCDF
1.2.36.7.8 HxCDF
?,3.4.6.7.8 HxCDF
Inhalation
Slope
Factor
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
80E-03
NA
NA
IDE -02
NA
30E-01
NA
NA
15E+05
7 5E+04
1 5E+04
1 5E»04
1 5E+04
1 5E»03
1 5E+02
1 5E*04
75E+03
75E+04
1 5E*04
1 5E»04
1 5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
002625
NA
0525
002625
NF
025
NA
0 02625
NA
000875
0 02625
') 1
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
1 75
175
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E 01
75E-03
NF
7 1E-02
NA
7 5E-03
NA
2 5E-03
7 5E-03
2 9E-02
2 1E*00
1 4E-02
NA
7 1E 02
10E-03
NA
50E-02
2 5E-02
NA
1 4E-02
NA
50E-01
5 OE-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E-06
55E08
1 2E-04
67E-08
67E-06
1 4E-08
1 4E-08
4 BE -05
14E-08
34E-05
55E-06
67E-08
55E-08
55E4W
1 2E-04
23E-05
1 4E-08
55E-06
55E-06
5 IE-OS
6 BE -06
6 1E-04
3 3E-04
55E-08
30E-08
13E-05
1 3E-05
1 9E-05
25E-04
55E-06
55E-06
64E-05
25E-04
3 BE -04
55E-08
106E-11
678E-11
895E-11
1 66E-10
1 09E 10
1 24E 09
615E09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
W3avg
W3avg
W3ivg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3ivg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
\rV3avg
Adult
Cancer
Risk
NT
NT
NT
NT
1 OE-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E-13
1 7E-12
1 6E-13
NT
NT
NT
NT
NT
NT
1 1E-12
1 7E-13
NT
NT
SSE-14
NT
1 1E-10
NT
NT
25E-12
79E 12
2 1E 12
38E 12
25E 12
29E 12
1 4E 12
20E 12
40E 12
54E-11
33E 11
3 IE 11
35E 11
Child :
Cancer
Risk
NT
NT
NT
NT
25E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
55E-13
43E-12
40E-13
NT
NT
NT
NT
NT
NT
2 7E 12
43E-13
NT
NT
2 1E-13
NT
2 8E-10
NT
NT
63E-12
20E 11
52E 12
96E-12
63E 12
72E 12
36E 12
5 IE 12
1 OE 11
1 4E 10
83E 11
77E 11
87E 11
School-age
Cancer
Risk
NT
NT
NT
NT
1 5E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E-13
26E-12
24E-13
NT
NT
NT
NT
NT
NT
1 7E-12
26E-13
NT
NT
13E-13
NT
1 7E-10
NT
NT
38E 12
1 2E-11
3 IE 12
5 BE 12
3BE 12
4 3E 12
22E 12
3 1E-12
60E 12
82E II
50E 11
47E 11
53E 11
Far met
Cancer
Risk
NT
NT
NT
NT
22E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
49E-13
3 BE 12
36E-13
NT
NT
NT
NT
NT
NT
25E-12
38E-13
NT
NT
19E-13
NT
2 5E-10
NT
NT
56E-12
1 8E-11
46E-12
86E-12
56E 12
64E 12
32E-12
45E 12
89E-12
1 2E 10
74E 11
69E 11
7 BE- 11
                                                                                                                                            Adult      Child   School-age   Farmer
                                                                                                                                          Noncancer  Noncancer Noncancer  Noncancer
                                                                                                                                             HQ        HQ        HQ        HQ
NT
4 6E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 4E-07
88E-09
NT
44E-10
BSE -09
NT
38E-09
NT
88E-09
NT
25E4J7
1 IE-OS
26E-07
19E-09
46E-09
NT
21E-09
15E-07
NT
59E-08
27E-09
NT
54E-08
NT
92E-09
1.3E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
tjr
NT
NT
1 7E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E-06
33E-08
NT
1 7E-09
33E-08
NT
1 4E 08
NT
33E-08
NT
92E417
41E-08
97E47
69E-09
1 7E-08
NT
79E-09
56E-07
NT
2 2E-07
9 9E-09
NT
2.0E-07
NT
3 4E-08
5.0E-10
NT
NT
NT
NT
NT
NT
HI
NT
NT
rn
NT
m
riT
NT
10E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
12E-08
20E-08
NT
1 OE-09
2 OE-OB
NT
86E-09
NT
20E-08
NT
56E-07
25E48
5 BE 07
42E-09
IDE -08
NT
4 BE -09
3.4E07
NT
1 3E-07
6 OE-09
NT
1 2E-07
NT
21E4)8
30E-10
NT
NT
NT
NT
NT
NT
NT
(IT
NT
NT
NT
NT
NT
NT
4 6E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
54E^)7
8 BE -09
NT
44E-10
8 BE -09
NT
3 BE -09
NT
88E-09
NT
25E^)7
1 IE-OS
26E47
19E09
46E-09
NT
21E49
15E-07
NT
59E-08
27E^9
NT
5 4E-08
NT
92E09
1 3E-10
NT
NT
NT
NT
tIT
NT
NT
NT
NT
NT
NT
NT
(IT
'olume V. Appendix V-14
-------
TABLE  12  Average Inhalation Risk-; and Noncancei HOs in Subaipa W3
CHEMICAL
1 2 3.7,8.9 HxCDF
1.2. 3.4 6.7.8 HpCDF
l.2.3,4.7.8.9-HpCDF
OCDF
Dioxtn TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (Irivalent)
Copper
Lead
Mercury (and MeHg)
Mickel
Selenium
Silver
Thallium
!mc
Hydrogen chloride
Total nitrogen oxides (NO)
Total sulfur oxides (SOx)
'articulate matter
hospitable particulates
Inhalation
Slope
Factor
(mg/kg-d)"- 1
1 5E*04
1 5E«03
1 5E»03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
OOOO075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E05
36E05
1 3E 03
1 3E-04
1 3E 03
25EO!
NA
NA
2 1E 05
50E 03
1 3E 03
1 3E 03
1 BE 05
75E 02
50E 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E 09
1 89E 08
428E 08
24E-04
42E 06
37E 05
1 5E-04
33E 08
16E-05
71E-07
7 IE 07
94E 05
43E 05
1 4E 03
50E 06
4 7E 04
1 5E-05
34E 05
1 2E-04
32E-02
24E+00
9 1E-02
72E02
72E-02
Subarei
W3avg
W3avg
W3avg
W3avg

W3avg
W3avg
W3avg
WSavg
W3avg
W3avfl
W3avg
W3ivg
W3avg
W3avg
W3avg
W3avg
W3*vg
W3avg
W3»vg
W3avg
W3evg
W3avg
\M3avg
W3avg
W3avg
Off-site
Vapor
Cone
(ug/m3)
1 3E-11
4 IE 10
54E 11
83E 10
1 9E 09
1 IE 05
1 BE 07
1 BE 06
66E 06
1 5E 09
7 OE-07
3 1E-08
3 IE 08
4 IE 06
1 9E-06
62E-05
22E 07
2 IE 05
66E 07
1 5E 06
53E-06
1 4E 03
1 1E-01
40E-03
3 2E 03
32E 03
Cancer
Adult
Dose
(mg/kg-d)
45E 16
1 4E 14
1 9E 15
29E 14
66E 14
37E-10
65E-12
57E 11
23E-10
5 1E-14
25E-11
1 1E-12
1 1E-12
1 5E 10
67E 11
22E09
7 7E-12
73E-10
23E 11
53E 11
1 9E-10
50E08
3 7E 06
1 4E 07
1 IE 07
1 IE 07
Cancer
Child
Dose
(mg/kg-d)
1 1E-15
36E-14
4 7E-15
73E 14
1 7E 13
93E-10
1 6E 11
1 4E 10
58E 10
1 3E 13
62E-11
27E 12
27E 12
36E 10
1 7E 10
54E09
19E-11
1 BE 09
5 BE 11
1 3E (0
46E-10
1 2E 07
93E-06
35E07
2 BE 07
2 BE -07
Cancel
School-age
Dose
(mg/Kgd)
6 BE 16
22E-14
28E-15
44E 14
10E-13
56E-10
9BE-12
86E-11
35E 10
77E-14
37E-11
1 7E-12
1 7E 12
22E-10
1 OE-10
3 3E 09
1 2E 11
1 IE 09
35E 11
79E 11
28E-10
7 5E 08
56E-06
2 1E 07
1 7E-07
1 7E-07
Cancer
Farmer
Dose
(mg/kg-d)
1 OE-15
32E 14
42E 15
65E 14
1 5E 13
83E-10
1 4E-11
1 3E-10
52E-10
1 1E-13
55E-11
24E-12
24E-12
32E 10
1 5E-10
46E-09
1 7E-11
1 6E 09
52E 11
1 2E 10
41E-10
1 1E 07
8 3E 06
3 IE 07
25E-07
25E 07
Noncancer
Adult
Dose
(mg/kg-d)
35E 15
1 IE 13
1 5E-14
23E 13
52E-13
29E-09
51E-11
45E-10
18E-09
40E-13
1 9E-10
86E-12
B6E-12
1 1E-09
52E-10
1 7E-06
60E 11
57E09
1 BE 10
4 IE 10
1 4E 09
3 9E-07
29E 05
1 1E 06
8 7E-07
8 7E-07
Noncancer
Child
Dose
(mg/kg d)
1 3E-14
42E 13
55E 14
85E 13
19E-12
1 1E-08
1 9E 10
1 7E-09
6 BE 09
15E 12
72E-10
32E 11
32E-11
42E-09
1 9E-09
6 3E-08
23E-10
2 IE 08
6 BE 10
1 5E-09
54E 09
1 4E-06
1 1E-04
4 1E-06
32E 06
32E-06
Noncancer
School-age
Dose
(mg/kgd)
BOE 15
25E-13
33E 14
52E 13
1 2E-12
6 5E 09
1 1E-10
1 OE 09
4 IE 09
90E-13
44E 10
19E 11
1 9E-11
26E-09
1 2E 09
38E08
1 4E-10
1 3E 08
4 1E 10
93E 10
33E-09
8 7E 07
6 6E 05
2 5E 06
20E 06
20E 06
Noncancer
Farmer
Dose
(mg/kg d)
35E-15
1 1E 13
1 5E 14
23E 13
52E 13
29E09
51E 11
45E 10
1 BE 09
40E 13
19E 10
86E 12
86E 12
1 IE 09
52E 10
1 7E 08
60E 11
57E 09
1 8E 10
4 IE 10
1 4E 09
39E 07
29E 05
1 IE 06
8 7E 07
8 7E 07
JOTES
  NA * Not applicable
  NF = Not round
  NT = No toxicity information
  HQ » Huard quotient
  HI  = Huard index
 olume V Appendix V-
-------
TABLE 12  Average Inhalation Risks and Noncancet HOs in Subaiea W3
CHEMICAL
Acenaphthene
Acenaphthylene.
Acetaldehyde
Acetone
Acetophenone
Acrylonitrile
Anthracene
Benzene
Benzole acid
Benzotoichkxkfo
Benzo(a)anthracene
Benzo(a)pyren»
Benzo(b)fluoranthene
Benzo(g,h,l)perytene
Benzo(k)fluoranthene
Bis(2-€hloroetho>fy) methane
Bis(2^hloroethy))ether
Bls(2-chloroisopropyl)ether
Bis(2 -ethylhexy1)phthalale
Bromodichloromethane
Bromoform
Bromomethane
Bromodiphanyt ether, p-
Butanone. 2- (Methyl ethyl ketone)
Butylbenrylphthalate
Carbon disuHide
Carbon tetrachloride
Chlordane
Chloro-3-methylphenol, 4-
Chloroaniline, p- (4-Chloroaniline)
Chlorobenzene
Chlorobenzilate
Chloroethine (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthalene, beta
Chlorophenol. 2- x:
Chlorodipheny) ether, 4-
Chrysene
Cresol. m-
Cresol, o- (2-Methytphenol)
Cresol. p-
Crotonaldehyde
Cumene
DDE. 4.4'-
Dibenz(a.h)anthracene
Dibromocnloromethane
Dichlorobenzene. 1 .3-
Dichlorobenzene. 1.4-
Dichlorobenzene. 1.2-
Dichlorobenzidme. 33
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/Vg d)*-1
NA
NF
7 7E43
NA
NA
24E^)1
NA
296-02
NA
NA
NA
NA
NA
NA
NA
NA
f 1E*00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
27E-01
NA
8 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02825
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
0 04375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E^)4
25E 02
25E 02
1 4E 04
7 5E-02
43E-04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE-02
50E 03
50E 03
50E-03
36E-04
NA
7 IE 02
50E 02
7 IE 04
1 4E-04
1 5E-05
NF
10E-03
1 4E-03
5 OE-03
71E-01
2 5E-03
NA
2 OE 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
64E 04
NA
NA
50E 03
NA
57E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E-06
67E-06
30E 04
29E-03
29E04
20E^M
55E-06
1 5E-05
1 1E-05
32E-05
S5E-06
55E-06
55E-06
55E-08
55E-06
6 7E-08
1 3E-05
6 7E-06
37E05
1 OE-04
55E-06
49E-04
87E-06
5 IE-OS
55E^)6
89E-05
1 6E-04
55E-07
67E-O6
67E-06
55E-06
37E-O5
4 9E-04
27E-04
25E-04
67E-06
55E-06
67E 06
55E 06
55E 06
55E-06
55E 06
1 4E 04
55E 06
55E 07
55E 06
2 6E 05
55E 06
55E 06
55E 06
33E 05
4 7£ 08
Subarea
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3 avg
W3avg
W3avg
W3avg
W3 avg
W3avg
W3 avg
W3avg
W3 avg
Adult
Cancer
Risk
NT
NT
36E-12
NT
NT
74E-11
NT
66E-13
NT
NT
NT
NT
NT
NT
NT
NT
23E-11
NT
NT
NT
33E-14
NT
NT
NT
NT
NT
1 3E-11
1 1E-12
NT
NT
NT
1 6E-11
NT
33E 11
24E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
fJT
NT
NT
m
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
89E-12
NT
NT
1 9E-10
NT
16E-12
NT
NT
NT
NT
NT
NT
NT
NT
56E-11
NT
NT
NT
82E-14
NT
NT
NT
NT
NT
32E-11
27E-12
NT
NT
NT
39E-11
NT
83E-11
60E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
fIT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
54E-12
NT
NT
1 1E-10
NT
1 OE-12
NT
NT
NT
NT
NT
NT
NT
NT
34E-11
NT
NT
NT
49E-14
NT
NT
NT
NT
NT
19E-11
1 7E-12
NT
NT
NT
23E-11
NT
50E-11
36E-12
NT
NT
NT
NT
NT
NT
NT
NT
HI
NT
(IT
in
NT
NT
NT
tIT
NT
Farmer
Cancer
Risk
NT
NT
8 OE-12
NT
NT
1 7E-10
NT
1 5E-12
NT
NT
NT
NT
NT
NT
NT
NT
50E-11
NT
NT
NT
73E-14
NT
NT
NT
NT
NT
29E-11
25E-12
NT
NT
NT
35E-11
NT
74E-11
53E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
m
fir
NT
tIT
NT
(IT
rir
                                                                                                                                             Adult      Child   School-age   Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HO        HQ
5 4E-09
NT
56E-06
1 4E-06
1 4E-07
1 7E-05
88E-10
4 1E-07
1 4E-10
NT
NT
NT
NT
NT
NT
NT
NT
81E-09
90E-08
25E^)7
1 3E-08
1 7E-05
NT
876-09
1 3E-09
1 5E-06
13E-05
44E-07
NT
81E-08
46E-08
69E-08
83E-09
1 3E-06
NT
40E-09
53E-08
NT
NT
53E-09
53E-09
5 3E-08
NT
1 OE 07
NT
NT
63E-08
NT
1 2E 09
4 6E 09
tIT
til
2 OE-08
NT
2 IE-OS
52E06
5 3E-07
64E-05
33E09
15E-06
51E-10
NT
NT
NT
NT
NT
NT
NT
NT
3 OE-08
3 3E-07
9 3E-07
5 OE 08
62E05
NT
326-08
50E09
S6E-06
50E05
1 7E-08
NT
30E-07
1 7E-07
3 3E-07
3 1E-08
48E-06
NT
1 5E-08
2 OE-07
NT
NT
20E-OB
20E 08
2 OE-07
NT
39F 07
NT
NT
? 4F 07
NT
4 3E 09
1 7F 06
til
m
1 2E-08
NT
1 3E-05
32E-06
3 2E-07
3 8E-05
2 OE-09
9 3E-07
31E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 8E 08
2 OE-07
S6E-07
3 OE-08
37E-05
NT
20E08
30E 09
34E-06
30E-05
1 OE-06
NT
1 BE 07
1 OE-07
2 OE-07
1 9E 08
29E-06
NT
9 1E-09
1 2E-07
NT
NT
1 2E-08
1 2E 08
1 2E-07
NT
? IF. 07
NT
NT
1 4E 07
NT
2 6E 09
1 OF. 08
NT
NT
5 4E 09
NT
5GE06
1 4E 06
1 4E 07
1 7E-05
66E-10
4 IE 07
1 4E-10
NT
NT
NT
NT
NT
NT
NT
NT
B1E-09
90E 08
2 5E-07
1 3E-08
1 7E-05
NT
87E-09
1 3EC3
1 5E-08
1 3E-05
4 4E-07
NT
8 IE 08
4 6E 08
8 9E 08
8 3E-09
1 3E 06
NT
4 OE-09
5 3E-08
NT
NT
53E 09
53E-09
5 36 08
NT
1 OE-07
NT
NT
6 3E 08
NT
1 2E 09
4 BE 09
III
(IT
Volume V. Appendix V-14
-------
TABLE 12  Average Irk,    jn Risks and Noncancei HQs in Subaiea W3
V  ,/'
CHEMICAL
1.2.3.7.8.9-HxCDF
1.2.3.4,6.7.6-HpCDF
1,2,3,4.7.8.9-HpCDF
OCDF
Oloxfn TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hcxavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Partlculate matter
Resplrable particulates
Inhalation
Slope
Factor
(mg/kg-d)*-1
1 5E+04
1 5E+03
1 5E»03
1 5E+02

MA
MA
SO
MA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0 004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E-05
13E-03
1 3E-04
1 3E-03
25E-01
NA
NA
2 IE-OS
50E-03
1 3EO3
1 3E 03
1 8E-05
7 5E 02
50E-04
NA
NA
NA
NF
Emission
Rale
(g/sec)
2 93E-10
930E-09
1 22E-09
1 89E-08
4 28E-08
24E-04
426-06
37E-05
15E-04
336-08
166-05
71E-07
716-07
94E-05
43E-05
1 4E 03
506-06
4 7E-04
1 5E-05
34E-05
1 2E-04
3 2E-02
24E+00
916-02
726-02
726-02
Subarea
W3avg
W3avg
W3avg
W3avg

W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3avg
W3«vg
W3avg
Adult
Cancer
Risk
68E-12
22E-11
28E-12
44E-12
22E-10
NT
NT
296-09
NT
436-13
1 5E-10
4 56-1 1
NT
NT
NT
NT
656-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
1 7E-11
54E-11
71E-12
1 1E-11
54E-10
Nf
NT
71E-09
NT
1 1E-12
38E-10
1 1E-10
NT
NT
NT
NT
16E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
1 OE-11
33E-11
43E-12
66E-12
33E-10
NT
NT
436-09
NT
65E-13
236-10
6.86-11
NT
NT
NT
NT
986-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Faimer
Cancer
Risk
1 5E-11
48E-11
63E-12
98E-12
4 8E-10
NT
NT
64E-09
NT
95E-13
346-10
1 06-10
NT
NT
NT
NT
1 46-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NOTES:
  NA - Not applicable
  NF-Not found
  NT " No loxlcity information
  HQ > Hazard quotient
  HI  -Hazardindex
                                                                               Total Risk   4 8E-09    1 2E-08    7 36-09    1  16-08
                                                                                                                                             Adult      Child    School-age  Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HQ        HQ
NT
NT
NT
NT
NT
NT
516-07
59E-06
516-05
326-10
15E-O6
68E-09
34E-11
NT
NT
79E-04
12E-08
456-08
1 4E-07
23E-05
1 9E-O8
77E-04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
196-06
22E05
196-04
1 26-09
586-06
2 66-08
1 36-10
NT
NT
296-03
4 56-08
17605
5 4E-07
87E05
7 2E-08
2.96-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 16-08
1 36-05
1 16-04
726 10
356-06
156-08
77E-11
NT
NT
t 86-03
2 7E 08
10E-05
3 3E 07
53E05
446-08
1 76-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 16-07
596-08
51605
326 10
156-06
686-09
346-11
NT
NT
796-04
1 26-08
456-06
1 46-07
23605
196-08
77E-04
NT
NT
NT
NT
                                                                                                                                   Total HI    19E-03    70E-03   4 2E 03    1 9E 03
Volume V. Appendix V-14
-------
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TABLE 13  Maximum Inhalation Risks and Noncancer HQs in Subaiea E1
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrylonltrile
Anthracene
Benzene
Benzole acid
Benzotrichlotlde
Benzo(a)anthracene
Benzojajpyrene
Bertto(b)fluoranthene
Beruo(g ,h .Open/tone
Benzo(k)fluoranthene
Bis(2-chloroethoxy) methane
Bls(2-chloroethyl)ether
Bls(2-chlorolsop»opyl)erher
Bls(2-««hylhexyT)phthalate
Bromodlchtoromethane
Bromoform
Bromomethane
Bromodiphenyl ether, p-
Butanone. 2- (Methyl ethyl ketone)
Butylbeniytphthalate
Carbon disuffide
Carbon tetrachloride
Chlordane
Chloro-3-methylphenol, 4-
Chloroaniline. p- (4-Chloroaniline)
Chlorobenzene
Chlorobenzilate
Chloroethane (Ethyl chloride)
Chloroform
Chloromettiane
Chloronaphthalene. beta
Chlorophenol, 2- H
Chlorodlphenyl ether. 4- '
Chrysene
Ctejol. m-
Cresol. o- (2-Melhylphenol)
Cresol, p-
Crotonaldehyde
Cumene
DDE. 4.4'-
Dibenz(a,h)anthracene
Dibromochlorometnane
Dichlorobenzene. 1,3-
Dichlorobenzene. 1.4-
Dichlorobenzene. 1.2-
Dichlorobenzidme. 3.3'-
Dichlofobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)«-1
NA
NF
7 7E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E03
NA
NA
NA
NA
NA
53E4)2
1 3E»00
NF
NA
NA
2.7E-01
NA
8 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA •
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00675
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00)75
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E-04
2 5E-02
25E-02
14E-04
75E-02
43E-04
IDE tOO
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E-03
50E-03
50E-03
36E-04
NA
71E-02
5 OE 02
7 1E^>4
1 4E-04
1 5E-05
NF
1 OE^)3
1 4E 03
5 OE-03
71E-01
25E-03
NA
20E-02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
64E-04
NA
NA
50E 03
NA
57E02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E-06
67E-06
30E-04
2 9E-03
29E-04
20E-04
55E-06
. 1 5E-05
1 IE-OS
32E-05
55E-06
55E-06
S5E-06
SSE^H
55E-08
67E06
1 3E-05
67E-06
37E-05
10E-04
55E-06
49E-04
67E4W
5 IE-OS
55E-06
89E-OS
16E-04
55E-07
67E-06
67E-06
55E-08
37E-05
4 9E-04
2 7E-04
2 SE 04
67E-06
55E-06
67E-06
55E-06
55E-06
55E-06
55E-06
1 4E 04
55E-06
55E 07
55E06
26E 05
55E 06
55E 06
55E 06
3 3E 05
4 7E 08
Subarea
El max
El max
E1 max
El max
El max
El max
El max
El max
El max
El max
El max
E1 max
El max
El max
El max
El max
El max
El max
El max
Et max
El max
El max
E1 max
El max
Et max
El max
E1 max
El max
E1 max
El max
El max
El max
El max
El max
El max
Et max
El max
El max
El max
El max
E1 max
El max
El max
El max
E 1 max
El max
El max
El max
Et max
E1 max
E 1 max
E 1 max
Adult
Cancer
Risk
NT
NT
74E-11
NT
NT
1 5E-09
NT
1 4E-11
NT
NT
NT
NT
NT
NT
NT
NT
47E-10
NT
NT
NT
68E-13
NT
NT
NT
NT
NT
2 7E-10
23E-11
NT
NT
NT
32E-10
NT
69E-10
49E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
1 9E-10
NT
NT
38E-09
NT
34E-11
NT
NT
NT
NT
NT
NT
NT
NT
12E-09
NT
NT
NT
1 7E-12
NT
NT
NT
NT
NT
66E-10
57E-11
NT
NT
NT
80E-10
NT
17E-09
t 2E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
1 1E-10
NT
NT
23E-09
NT
21E-11
NT
NT
NT
NT
NT
NT
NT
NT
7.1E-10
NT
NT
NT
10E-12
NT
NT
NT
NT
NT
40E-10
34E-11
NT
NT
NT
48E-10
NT
10E-09
74E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NI
NT
NT
Nf
tu
NT
NT
Farmer
Cancer
Risk
NT
NT
1 7E-10
NT
NT
3 4E-09
NT
30E-11
NT
NT
NT
NT
NT
NT
NT
NT
10E-09
NT
NT
NT
1.5E-12
NT
NT
NT
NT
NT
59E-10
5.1E-11
NT
NT
NT
7.2E-10
NT
15E-09
1.1E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                            Adult      Child   School-age   Farmer
                                                                                                                                          Noncancer Noncancer Noncancer Noncancer
                                                                                                                                             HQ       HQ       HO       HQ
1 1E-07
NT
1 2E-04
2 9E-05
29E-06
3 5E-04
1 BE 08
86E-06
2 BE -09
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-07
19E-06
S IE-OS
2 7E-07
3 4E-04
NT
1 BE -07
27E-08
31E05
2 BE 04
9 IE-OB
NT
17E-08
96E-07
1 BE -06
1 7E-07
27E-05
NT
B3E-08
1 1E-06
NT
NT
1 1E-07
1 1E-07
1 IE-OB
NT
2 IE-OB
NT
NT
1 3E 06
NT
2 4E 08
9 BE -08
NT
NT
4 2E-07
NT
4 4E 04
1 1E-04
1 IE 05
1 3E-03
6 8E-08
3 2E-05
1 IE-OS
NT
NT
NT
NT
NT
NT
NT
NT
6 2E 07
69E-06
9E-05
OE-06
3E-03
NT
6 7E-07
OE-07
2E-04
OE-03
34E-05
NT
62E-06
3 BE 06
69E-06
6 4E-07
99E-OS
NT
3 IE 07
41E-06
NT
NT
4 IE 07
4 IE 07
4 1E-06
NT
BOE 06
NT
NT
49F 06
NT
90E 08
3 RE 07
NT
NT
2 5E-07
NT
2 BE 04
BSE 05
6 BE 06
8 OE 04
4 1E-08
1 9E-05
64E-09
NT
NT
NT
NT
NT
NT
NT
NT
3 8E 07
42E-06
1 2E 05
6 2E-07
77E-04
NT
4 1E-07
62E08
70E-05
6 2E 04
2 IE-OS
NT
3 BE 06
22E06
4 IE 06
39E07
BOE -05
NT
1 9E 07
2 5E-06
NT
NT
25E 07
25E 07
25E 06
NT
4 BE 06
NT
NT
3 OE-06
NT
54E 08
2 2F.-07
NT
NT
1 1E-07
NT
1 2E-04
29E-05
29E-06
3 5E 04
1 BE -08
86E-06
2 BE -09
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-07
19E-06
5 IE 06
2 7E 07
3 4E-04
NT
1 BE 07
2 7E-08
3 IE-US
2 BE 04
91E-06
NT
17E06
96E07
16E-06
1 7E 07
2 7E-05
NT
83E 08
1 1E-06
NT
NT
1 IE 07
1 IE 07
1 IE-OB
NT
2 1E-06
NT
NT
1 3E-06
NT
24E 08
96E 08
NT
NT
Volume V. Appendix V-14
-------
CO
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Noncancer Noncan
School age Farme
Dose Dose
(mg/kg d) (mg/kg
oncan
Child
Dose
(mg/kg-
Noncancet
Adult
Dose
(mg/kg d)
Cance
Farme
Dose
mg/kg-
Cancer
chool age
Dose
mg/kg d)
Cancer
Child
Dose
mg/kg-d)
Cance
Adult
Dose
mg/kg
Off site
Vapor
Cone
(ug/m3)
Emissi
Rate
(g/sec
alati
RfD
g/kg-
AC
/m
nhalalic
Slope
Factor
g/kg-d
CHEMICAL
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TABLE 13  Maximum Initiation Risks and Noncancet HQs in Subaiea E1
CHEMICAL
Dichlorodffluorometnane
Dichlotoettian*. 1.1- (Ethylidene dichloride)
Dichloioflttiane, 1 ,2-
Dichloioethene, 1,1- (\finylidine chloride)
DichlorooJhen* (tram). 1,2-
Oichlorophcnol. 2,4-
Dichloropropane. 1,2- (Propylene dichloride)
DichloroprofMfM (els), 1,3-
Dichloroptopene (bans), 1 .3-
Dieth/lphthalate
Dimethoxybenztdlne, 3,3'-
Dimethylpheno), 2,4-
DtmelnylphtMat*
Dt-n-butytphlhalat*
Dinltrotoluerw, 2.6-
Dlnrbo-2-m«thy1phenol. 4.6-
DtnMrophenol. 2.4-
Dinrbotoluene. 2.4
Diowine. 1,4-
Di(n)octy) phthalate
D, 2.4-
Ethyt mathacrylate
ElhylUniene
Ethylene dibromlde
Ethylene oxide
Ethylene (hkuirea
Fluofanthene
Fluorene
Formaldehyde
Furfural .
Heptachtof
Heptachlorobiphenyi
Hexachlorobenzene
Hflxachlorobipheny)
Hexachlorobutadlene
Hexachlorocyctohexane. gamma (Lindane)
Hexachlorocyclopentadleni)
Hexachloroeihane
Hexschlorophene
Hexanone. 2-
lndeno(1.2,3-cd)pyrene
Kophotone
Maleic hydrazide
Methoxychlor
Methyl 1 butyl ether
Methyl-2-Pentanone. 4- (MIBK)
Methytene chloride
Methylnaphthalene. 2-
Monochtorobiphenyl
Naphthalene
NHroanilin'e. 2-
Nitioaniline, 3-
Inhalation
Slope
Factor
(mg/kg-d)*- 1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E-01
35E^>1
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
7 6E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF •
NA
NA
NA
NF
RAC
(mg/m3)
005
0125
NA
0007875
00175
0 002625
0001
0005
0.005
0.7
NA
00175
NA
00075
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RtD
(mg/kg-d)
1 4E-02
3 6E-02
NA
2 3E-03
5 OE-03
7 5E-04
29E-04
14E-03
1 4E-03
2 OE-01
NA
5 OE-03
NA
2 5E-02
25E-04
NF
5 OE-04
50E-04
NA
50E03
2 5E-03
2 3E 02
7 IE 02
1 4E-05
NA
20E-05
1 OE 02
1 OE-02
50E-02
3 6E-03
1 3E-04
NA
2 OE-04
NA
5 OE 05
7 5E 05
50E-06
25E04
7 5E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
flF
NA
1 OE 02
1 4E 05
tJF
Emission
Rate
(g/sec)
2 5E-04
1 3E 05
3E-05
3E-05
3E-05
5E-06
3E-05
3E-05
' 3E-05
7E-05
2E04
55E-06
55E-08
16E-OS
55E08
55E-06
55E06
55E-06
49E04
55E06
39E-05
2 5E 04
50E04
1 2E-04
31E-05
1 5E-10
55E-06
67E-06
6 1E-04
55E-06
5 5E-07
1 4E-08
55E-06
1 4E-08
1 OE-04
55E 05
55E06
55E06
32E 05
6 4E 05
55E06
67E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
67E 06
6 7E 06
Subarea
El max
E1 max
El max
El max
E1 max
El max
El max
E1 max
El max
El max
El max
El max
El max
El max
E1 max
El max
Et max
El max
El max
El max
E1 max
El max
E1 max
E1 max
El max
El max
El max
E1 max
El max
El max
El max
El max
E1 max
Et max
El max
El max
El max
El max
El max
El ma
El ma
E1 ma
El ma
Et ma
El m
El m
El m
El m
El m
El ma
El ma
El ma
Adult
Cancer
Risk
NT
NT
36E-11
48E-10
NT
NT
NT
52E-11
52E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 BE -09
34E-10
NT
NT
NT
88E-10
NT
79E-11
NT
28E-10
NT
25E-10
NT
NT
25E-12
NT
NT
NT
NT
NT
NT
NT
NT
2 IE 11
m
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
91E-11
1 2E-09
NT
NT
NT
1 3E-10
1 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E09
85E-10
NT
NT
NT
22E-09
NT
20E-10
NT
7 1E-10
NT
63E-10
NT
NT
61E-12
NT
NT
NT
NT
NT
NT
NT
NT
5 2f. 11
NT
NT
NT
NT
m
School-age
Cancer
Risk
NT
NT
55E-11
72E-10
NT
NT
NT
78E-11
7 BE- 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
42E-09
5 1E-10
NT
NT
NT
1 3E-09
NT
1 2E-10
NT
43E-10
NT
38E-10
NT
NT
37E-12
NT
NT
NT
NT
NT
NT
NT
NT
3 IE 11
HI
NT
(IT
NT
NT
Farmer
Cancer
Risk
NT
NT
81E-11
1 1E-09
NT
NT
NT
1 2E-10
1 2E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
62E-09
7 6E-10
NT
NT
NT
1 9E-09
NT
1 BE-10
NT
63E-10
NT
56E-10
NT
NT
55E-12
NT
NT
NT
NT
NT
NT
NT
NT
46E 11
NT
NT
in
NT
NT
                                                                                                                                           Adult      Child   School-age   Faimer
                                                                                                                                        Noncancer Noncancer Noncancer  Noncancer
                                                                                                                                           HQ       HQ        HQ        HQ
4 3E-06
8 7E-08
NT
1 4E-06
62E4)7
18E-06
1 1E-05
22E-06
22E-06
2 1E-08
NT
2 7E-07
NT
1 6E-07
S5E-06
NT
27E-06
27E-06
NT
27E-07
39E-06
27E-06
1 7E-06
2 OE-03
NT
18E-09
1 4E-07
1 7E-07
30E-06
3 BE -07
1 IE-OB
NT
69E-06
NT
5 OE 04
1 BE -04
27E^>4
S5E-06
1 1E-04
NT
NT
33E 08
2 3E-07
1 IE 07
1 5E 08
55E 07
46E 07
NT
NT
1 IE 07
1 ?E 04
NT
1 6E 05
3 3E-07
NT
52E4»
23E-06
68E-06
4 IE-OS
8 IE-OS
8 IE 06
78E-08
NT
10E-O6
NT
5 8E-07
20E-05
NT
10E-OS
1.0E-05
NT
10E06
14E-05
10E^»
BSE -OB
75E-03
NT
BSE -09
5fE-07
62E-07
1 IE OS
14E06
4 IE-OB
NT
26E-05
NT
1 9E 03
6 BE 04
10E4)3
2 OE 05
4 OE-04
NT
NT
1 2E 07
86E 07
4 IE 07
54E 08
20t 06
1 ?f 06
NT
NT
5 IE 07
4 4F 04
NT
97E06
2 OE-07
NT
31E-06
1 4E 06
4 IE 06
2 5E-05
49E06
49E-06
4 7E-08
NT
6 2E-07
NT
35E-07
12E05
NT
62E-06
62E-06
NT
6 2E 07
87E-OB
61E-06
39E06
45E03
NT
41E-09
3 IE 07
38E07
6 BE 06
B 7E 07
25E-06
NT
1 5E 05
NT
1 IE-OS
4 IE 04
6 2E 04
1 2E-05
2 4E 04
NT
NT
75E 08
52E 07
25E 07
33F 08
1 2E 06
1 OE 06
NT
NT
3 IE 07
26F 04
NT
43E-06
8 7E-08
NT
1 4E-06
6 2E 07
1 8E-06
1 IE-OS
22E06
22E-06
21E-08
NT
2 7E-07
NT
16E-OT
55E08
NT
27E-06
27E-06
NT
2 7E-07
39E06
27E-06
17E06
20E03
NT
1 8E 09
1 4E 07
1 7E 07
30E-08
3 BE -07
1 1E-08
NT
69E-OB
NT
50E 04
1 BE -04
27E-04
55EOB
1 1E-04
NT
NT
3 3E 08
23E 07
1 IE 07
1 5E 08
55E 07
4fiE 07
UT
NT
1 4E 07
1 ?E 04
NT
Volume V, Appendix V 14
-------
TABLE  13  Maximum Inhalation Risks and Noncancef HQs in Subarea £ 1
CHEMICAL
Nitroanlline, 4-
Nrtiobenzene
Nilrophenol. 2-
Nibophenol. 4-
N Nrtioio-di n butylamine
N Nrtroso-di-n-propytamin«
N NHrosodiphenylamin* (Oiphenylamme)
Nlonachlorobiphenyl
Octachlofobiphenyl
"entachloroberuene
P»nUch(oiobiph»nyl
P«ntachhMonttiob«nz«ne
°entachk>rophenol
Dhenanttirene
'henol
*yrene
iafrole (5-(2-Propenyl)-1,3 ben*odioxole)
jtyrene
Tetrachloroblphenyl
febachloroalhane. 1 .1 .1 .2-
Febachloioethane. 1.1.2.2
rebacnloroethene
'etoachloiophenol. 2.3 4.6
oluene
'richloto-1.2,2-tTifluoro«thane, 1 1.2-
rlchloroberuene, 1,2,4-
richlotobiphenyl
richloroethane. 1.1.1- (Methyl chloroform)
tichloroottiane. 1.1,2-
rlchloroelhene
richlorofluoromettiane
richloroph»nol, 2.4,5-
richlofophsnol. 2.4.6-
inyt acetate
Inyt chloride
ylene, m/p- (m/p-Oimethyl benzene)
ylene, o- (o CNmettiyl benzene)
,3.7.8-TCDD ;
2.3.7.8PCDD
2.3.4 7,8-HxCDD
2.3.6.7,8-HxCDD
i 2,3.7.8.9 HxCDD
2.3.4.6,7.8 HpCDD
COD
3 7 8 TCOF
2.3.7.8PCDF
3.4 7.8 PCDF
2.3 4.7 8 HxCDF
2 3 6 7.8 H*CDF
3.4 6 7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)« 1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E 02
20E^)1
20E 03
NA
NA
NA
NA
NA
NA
5 7E-02
60E 03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E+05
7 5E+04
1 5E«04
1 5E»04
1 5E+04
1 5E*03
1 5E*02
1 5E«04
75E«03
75E»04
1 5E»04
1 5E«04
1 5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
002625
NA
0525
0 02625
NF
025
NA
002625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E^)4
75E-03
NA
1 5E-01
75E-03
NF
7 1E^>2
NA
75E-03
NA
25E^J3
75E-03
29E 02
2 1E»00
1 4E-02
NA
7 1E^2
1 OE-03
NA
5 OE-02
25E4J2
NA
1 4E-02
NA
50E41
50E-01
NA
NA
NA
NA
NA
NA
NA
flA
NA
NA
NA
flA
fJA
Emission
Rate
(g'soc)
6 7E-06
55E06
6 7E 06
55E-06
1 2E 04
6 7E 06
6 7E 06
1 4E-08
1 4E-08
4 BE -05
1 4E 08
34E-05
55E-06
67E-06
55E-06
55E-06
1 2E 04
23E 05
1 4E 08
55E06
55E06
5 IE 05
68E 06
6 1E 04
3 3E 04
55E06
30E OS
1 3E^»
1 3E 05
1 9E 05
2 5E 04
55E06
55E-06
64E05
2 5E 04
3 BE 04
55E-06
1 08E-11
678E-11
895E 11
166E-10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
El maK
El max
El max
E 1 max
El max
El max
E1 max
El max
El max
El max
El max
El max
Et max
Et max
El max
El max
E1 max
El max
El max
E1 max
E1 max
El max
El max
Et max
El max
Et max
El max
El max
El max
El max
E1 max
E1 max
E1 max
El max
El max
El max
Et max
Et max
Et max
;E1 max
E1 max
El max
E t ma«
E1 man
E 1 ma<
E t ma«
E 1 max
E 1 max
E 1 ma«
E 1 mat
Cfl site
Vapor
Cone
(ug/m3)
6 IE 06
50E 06
6 1E 06
50E 06
1 1E 04
6 1E 06
6 IE 06
1 3E 08
1 3E 08
4 3E-05
1 3E 08
3 IE-OS
50E-06
6 1E-06
50E-06
50E 06
1 OE 04
20E-05
1 3E 08
50E 08
50E 06
47E^>5
62E-06
5 6E 04
30E 04
50E 06
2 7E 08
1 1E^»
1 IE 05
1 7E 05
22E04
50E06
50E-06
5 9E 05
2 2E-04
3 5E-04
5 OE-06
98E 12
62E 11
8 1E 11
1 5E 10
99E 11
1 IE 09
56E 09
80E 11
3 IE 10
4 2E 10
1 3E 09
1 2E 09
1 4E 09
Cancer
Adult
Dose
(mg/kg d)
2 IE 10
1 8E 10
2 1E-10
1 BE 10
39E 09
2 IE 10
2 IE 10
45E 13
45E 13
1 5E 09
45E 13
1 IE 09
1 8E-10
2 1E-10
1 8E 10
1 8E-10
3 7E-09
72E-10
45E-13
1 8E-10
1 BE 10
1 6E-09
22E-10
20E08
1 IE 08
1 BE 10
97E 13
40E-10
40E-10
60E-10
7 9E-09
1 8E-10
1 8E-10
2 1E-09
79E-09
1 2E-08
1 8E-10
35E-16
22E 15
29E 15
53E 15
35E 15
40E 14
20E 13
28E 15
1 IE H
1 5E 14
46E 14
4 3E 14
4 BE 14
Cancer
Child
Dose
(mg'kg d)
53E 10
44E 10
53E 10
44E 10
97E 09
53E 10
53E 10
1 IE 12
1 IE 12
3 BE 09
1 1E-12
2 7E 09
44E 10
53E 10
44E 10
44E 10
92E 09
1 8E 09
1 IE 12
44E-10
44E-10
41E-09
54E-10
4 9E-08
2 6E-08
44E 10
24E-12
1 OE-09
10E-09
15E09
20E-08
44E-10
44E-10
51E-09
2 OE 08
3 OE-08
44E-10
86E 16
54E 15
71E 15
1 3E 14
87E 15
99E 14
49E 13
70E 15
28E 14
3 7f 14
1 IE 13
1 IE 13
1 2E 13
Cancer
School age
Dose
(mg/Vg d)
32E 10
2 7E 10
32E 10
2 7E 10
58E-09
32E 10
32E-10
68E-13
68E 13
23E-09
68E-13
1 6E 09
2 7E-10
32E-10
27E 10
27E-10
55E09
1 1E-09
6 BE 13
2 7E-10
2 7E-10
25E^)9
3 3E-10
30E08
1 6E-06
27E-10
1 5E-12
60E-10
60E-10
90E 10
1 2E-08
2 7E-10
2 7E-10
31E-09
1 2E-08
1 8E-08
27E-10
52E-I6
33E 15
43E 15
80E 15
53E 15
6QE 14
30E 13
42E 15
1 7E 14
23E 14
69E 14
6 4E 14
7 3E 14
Cancer
Farmer
Dose
(mg/kg d)
48E 10
39E 10
48E 10
39E 10
86E 09
4 BE 10
4 BE 10
10E 12
10E 12
34E-09
10E 12
24E-09
39E-10
48E-10
39E-10
39E-10
82E 09
1 6E-09
1 OE 12
39E 10
39E 10
37E09
4 BE 10
4 4E 08
2 3E-08
39E 10
22E 12
89E 10
89E-10
1 3E-09
1 7E-08
39E-10
39E-10
46E-09
1 7E-08
2 7E-08
39E-10
77E 16
4 BE 15
64E 15
1 2E 14
7 BE 15
88E 14
44E 13
62E 15
25E 14
3 3E 14
1 OE 13
9r>F 14
1 IF 11
Noncancet
Adult
Dose
(mg/kg d)
1 7E 09
1 4E 09
1 7E 09
1 4E 09
30E 08
1 7E 09
1 7E 09
35E 12
35E-12
1 2E 08
35E 12
84E09
14E09
1 7E 09
1 4E 09
1 4E 09
29E 08
56E-09
35E-12
1 4E 09
1 4E 09
1 3E 08
1 7E09
1 5E-07
82E 08
1 4E-09
75E-12
3 IE 09
3 IE 09
46E 09
61E08
1 4E 09
1 4E 09
1 6E 08
6 IE 08
95E 08
1 4E 09
27E 15
1 7E-14
22E 14
41E 14
2 7E 14
3 IE 13
1 5E 12
2 2E 14
86E 14
1 2E 13
36E 13
3 3E 13
TBF 13
Noncancer
Child
Dose
(mg/kg d)
62E 09
5 1E 09
62E 09
5 1E 09
1 IE 07
62E09
62E09
1 3E 11
1 3E 11
44E08
1 3E 11
3 IE 08
5 IE 09
62E09
51E-09
51E-09
1 1E^>7
2 IE 08
1 3E 11
51E-09
51E^)9
4 BE 08
63E49
57E^)7
31E^)7
5 IE 09
2BE-11
1 2E 08
1 2E 08
1 7E 08
23E07
51E09
5 IE 09
6 OE 08
23E07
35E 07
5 IE 09
1 OE 14
63E 14
83E 14
1 5E 13
1 OE 13
1 ?E 12
5 7E 12
8 ?E 14
3 ?F 13
4 IE 13
1 IE 12
1 ?f 12
1 -If 12
Noncancer
School age
Dose
(mg'kg d)
38E 09
3 IE 09
3 BE 09
3 1E 09
6 BE 08
3 BE 09
3 BE 09
79E 12
79E-12
2 7E 08
79E-12
19E08
3 IE 09
3 BE -09
31E09
3 IE 09
65E08
1 3E 08
79E-12
31E-09
3 IE 09
29E08
3 BE 09
34E^)7
1 9E 07
3 IE 09
1 7E 11
70E 09
70E 09
1 OE 08
1 4E 07
3 IE 09
3 IE 09
36E 08
1 4E 07
2 1E^)7
3 IE 09
6 IE 15
3 BE 14
50E-14
93E 14
6 IE 14
70E 13
35E 12
49E 14
1 9E 13
26E 13
80E 13
75E 13
B^F 13
Noncancer
Farmer
Dose
(mg/kg d)
1 7E 09
1 4E 09
1 7E 09
1 4E 09
3 OE-08
1 7E 09
1 7E 09
35E 12
35E 12
1 2E 08
35E 12
84E09
1 4E 09
1 7E 09
1 4E-09
1 4E 09
29E^»8
56E09
35E 12
4E-09
4E-09
3E48
7E09
5E07
6 2E 08
t 4E 09
75E 12
31E09
3 IE 09
46E09
61E08
1 4E 09
1 4EX)9
1 6E 08
6 IE 08
95E08
t 4E 09
27E 15
1 7E 14
2 2E 14
4 IE 14
2 11 14
3 IE 13
1 5E 12
22E 14
86E 14
1 2E 13
36E 13
3 3E 13
3BF 13
  >lume V. Appendix V-14
-------
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-------
T/ BLE 13  Maximum Inhalation Risks and Noncancei HOs in Subarea E 1
CHEMICAL
1 2.3 7,89HxCDF
1. 2.3.4 6.7.8 HpCDF
1.2.3.4. 7.8 ,9-HpCOF
OCDF
Dloxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavatent)
Chromium (bivalent)
Copper
Leid
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
; Hydrogen chloride
; Total nitrogen oxides (NOx)
I Total sulfur oxides (SOx)
J Partjculate matter
! Resplrable particulates
Inhalation
Slope
Factor
(mg/kg-d)"-1
1 5E+04
1 5E+03
1 5E+03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
HA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E 05
3 6E 05
1 3E 03
1 3E 04
1 3E 03
2 5E-01
NA
NA
2 1E 05
50E 03
1 3E 03
1 3E 03
1 BE 05
7 5E 02
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E 09
1 22E 09
1 89E 08
428E 08
24E-04
4 2E-06
37E-05
1 5E 04
3 3E 08
1 6E 05
7 IE 07
7 IE 07
94E 05
43E 05
1 4E 03
50E06
4 7E 04
1 5E 05
34E 05
1 2E 04
3 2E-02
24E*00
9 IE 02
7 2E-02
7 2E 02
Subarea
E 1 max
El max
El max
El max

El max
El max
El max
El max
El max
El max
El max
El max
El max
El max
El max
El max
El max
E1 max
E1 max
El max
E1 max
El max
El max
Et max
El max
Off site
Vapor
Cone
(ug/m3)
2 7E-10
85E 09
1 1E 09
1 7E-08

2 2E-04
38E-06
34E 05
1 4E 04
30E 08
1 5E-05
65E 07
65E 07
86E 05
39E 05
1 3E 03
46E 06
4 3E 04
1 4E 05
31E 05
1 1E-04
29E-02
22E+00
83E 02
66E 02
66E02
Cancer
Adult
Dose
(mg/kg-d)
94E 15
30E 13
39E 14
61E 13
1 4E-12
7 7E 09
1 3E-10
1 2E 09
4 8E 09
1 IE 12
51E-10
23E 11
23E 11
3 OE-09
1 4E 09
4 5E-08
1 6E-10
1 5E 08
48E 10
1 1E 09
3 8E 09
10E-06
7 BE -05
29E 06
23E 06
23E-06
Cancel
Child
Dose
(mg/kg-d)
2 3E-14
74E 13
97E-14
1 5E-12
34E 12
1 9E 08
34E 10
30E09
1 2E-08
26E 12
1 3E-09
57E-11
57E-11
75E 09
34E 09
1 1E-07
4 OE-10
3 BE 08
1 2E 09
27E-09
96E-09
26E06
1 9E-04
73E 06
57E 06
57E-06
Cancel
School age
Dose
(mgfkgd)
1 4E-14
45E-13
59E 14
9 IE 13
2 IE 12
1 2E-08
2 OE-10
1 BE -09
72E09
16E-12
77E-10
34E-11
34E-11
45E-09
2 IE 09
6 BE 08
24E-10
2 3E 08
72E-10
16E09
5 8E-09
1 5E-06
1 2E 04
44E-06
35E-06
35E-06
Cancel
Farmer
Dose
(mg/kg d)
2 1E 14
66E-13
87E 14
1 3E 12
30E 12
1 7E 08
30E 10
26E 09
1 IE 08
23E 12
1 1E-09
51E-11
51E-11
6 7E 09
3 IE 09
10E07
36E-10
33E 08
1 1E-09
24E09
BSE -09
23E-06
1 7E 04
65E 06
51E 06
51E06
Noncancei
Adult
Dose
(mg/kg-d)
7 3E-14
23E 12
30E 13
4 7E 12
1 IE 11
60E4)8
1 OE 09
92E 09
37E08
82E-12
4 OE-09
1 BE 10
1 BE 10
2 3E 08
1 IE 08
35E07
1 2E^)9
1 2E^)7
37E4)9
85E^)9
30E^)8
80E^6
60E-04
23E^)5
1 BE -05
18E-05
Noncancei
Child
Dose
(mg/kg d)
2 7E-13
87E 12
1 1E-12
1 BE 11
40E-11
2 2E 07
39E-09
3 4E 08
1 4E-07
31E 11
1 5E-08
66E-10
66E 10
8 BE 08
4 OE 08
13E 06
4 7E 09
44E 07
1 4E-08
32E08
1 1E-07
30E-05
2 3E-03
85E 05
6 7E 05
67E05
Noncancer
School-age
Dose
(mg/kg d)
1 6E-13
52E 12
69E 13
1 IE 11
24E 11
1 4E-07
2 4E 09
2 IE 08
8 4E 08
1 9E 11
9 OE-09
4 OE-10
40E 10
53E 08
2 4E 08
79E 07
2 BE 09
26E 07
84E09
1 9E 08
6 BE 08
18E05
1 4E 03
5 IE 05
4 IE 05
4 IE 05
Noncancer
Farmer
Dose
(mg/kg d)
7 3E-14
23E 12
30E 13
4 7E 12
1 1E-11
60E 08
10E09
92E09
37E4)8
82E 12
4 OE-09
1 8E-10
18E-10
2 3E 08
1 IE 08
35E07
t 2E 09
1 2E 07
37E09
85E09
30E 08
80E06
60E04
2 3E 05
1 BE 05
1 BE 05
  NA - Not applicable
  NF « Not found
  NT * No loxicrty information
  HO » Hazard quotient
  HI  * Hazard index
 olume V. Appendix V
-------
TABLE 13  MaximumV..jiation Risks and Noncancer HQs in Subarea E1
CHEMICAL
1,2.3.7.8.9 HxCDF
1, 2.3.4 6,7.8-HpCDF
1.2.3.4.7.8.9-HpCDF
OCDF
Dtoxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Parttculate matter
Resplrable participates
Inhalation
Slope
Factor
(mg/kg-d)"-1
1 5E+04
1 5E+03
1 5E+03
1 5E+02

MA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
0001 75
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E-05
1 3E-03
1 3E-04
13E-03
25E-01
NA
NA
21E05
SOE-03
1 3E-03
1 3E-03
18E-05
75E-02
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-O9
1 22E-09
1 89E-08
428E-08
24E-04
4 2E-06
37E05
15E-04
33E-08
16E-05
7 1E-07
7 1E-07
94E-05
43E-05
1 4E-03
50E-08
47E-04
15E05
34E-05
12EXM
3 2E-02
24E+00
9 IE 02
7 2E-02
72E-02
Subarea
Et max
E1 max
E1 max
El max

E1 max
El max
E1 max
El max
El max
El max
El max
El max
E1 max
E1 max
El max
El max
El max
E1 max
El max
El max
E1 max
El max
El max
El max
E1 max
Adult
Cancer
Risk
1 4E-10
45E-10
5SE-11
91E-11
45E-09
NT
NT
5.9E-08
NT
89E-12
31E-09
93E-10
NT
NT
NT
NT
1 3E 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
35E-10
1 1E-09
1 5E-10
23E-10
1 IE-OS
NT
NT
1 5E-07
NT
22E-11
7 BE -09
236-09
NT
NT
NT
NT
34E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
21E-tO
6 7E-10
8BE-11
1 4E-10
6 8E-09
NT
NT
89E-08
NT
13E-11
47E-09
ME -09
NT
NT
NT
NT
20E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
31E-10
99E-10
1 3E-10
20E-10
1 OE-08
NT
NT
1 3E-07
NT
20E-11
69E-09
2 1E-09
NT
NT
NT
NT
30E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NOTES:
  NA - Not applicable
  NF - Not found       *-
  NT « No toxictty Information
  HO • Hazard quotient
  HI -HazardIndex
                                                                               Total Risk   1 OE-07   2 5E-07   1 5E-07   2 2E-07
                                                                                                                                             Adult      Child   School-age   Farmer
                                                                                                                                           Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HQ        HO
NT
NT
NT
NT
NT
NT
1 OE-05
1 2E-04
10E-03
66E-09
32E-05
14E-07
7 1E-10
NT
NT
16E-02
2 5E-07
94E-05
30E-06
48E-04
40E-07
16E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E-05
4 6E-04
3 9E 03
25E-08
1 2E-04
5 3E-07
26E-09
NT
NT
61E-02
93E-07
35E44
1 IE-OS
1 BE 03
15E-06
80E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
24E^»
2 BE -04
2 4E-03
15E08
72E-05
32E-07
16E-09
NT
NT
37E42
5 6E-07
21E-04
6 BE 06
1 1E-03
90E-07
36E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 OE-05
1 2E-04
1 OE 03
66E09
32E05
1 4E 07
71E-10
NT
NT
1 6E 02
2 5E-07
94E05
30E06
4 BE 04
40E-Q7
16E-02
NT
NT
NT
NT
                                                                                                                                   Total HI   39E-02    1 4E-01   8 7E-02    39E-02
Volume V. Appendix V-14
-------
CD
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Noncancer Noncance
School age Farmer
Dose Dose
(mg/kg d) (mg/kg-d)
Child
Dose
g/kg d
Adult
Dose
mg/kg d)
nc
rm
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/kg
Do
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Cancer
Adult
Dose
mg'kg d)
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Rate
(g/sec)
lati
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RAC
mg/m3
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-------
TABLE 14  Maximum
                        on Risks and Noncancei HQs in Subarea E2
CHEMICAL
Acenaphthene
Acenaphthylene
Acelaldehyde
Acetone
Acetophenone
Acrylontbite
Anthracene
Benzene
Benzole acid
Benzotrtchtortde
Benzo(a)antfuacene
Benze(«)pyr«ne
Benzo(b)fluoranthene
Benzo{B.h.i)perylene
Benzo{k)fluoranthene
Bl»(2-chtoroerhoxy) methane
Bis(2-chk>roemyf)elher
Bis(2-chk*olsopropyr)ether
Bls(2-ethythexyl)phlhalite
Bromodlchloromethane
Bromoform
Bromomettiane
Biomodlphenyt ether, p-
Butanone. 2- (Methyl elhyf ketone)
Butyl be nzylphthalale
Carbon dlsulfide
Carbon tetrachloride
Chlordane
Chkxo-3-methylphenol. 4-
Chloroanlllne, p- (4-Chloroanlllne)
Chkxobenzene
Chlorobenzllate
Chloroethane (Ethyl chloride)
Chloroform
Chloromethane
Chtoronaphthalene. beta
Chtofophenol, 2-
Chlorodiphenyl ether, 4- >,
Chrysene
Cresd. m-
Cresol, o- (2-Methylph«nol)
Cresol. p-
Crotonaldehyde
Cumene
DDE, 4.4'-
Dibenz(a.h)anthracene
Dibromochloromethana
Dichlorobenzene. 1.3-
Dichlorobenzene. 1 .4-
Dichlofobenzene, 1,2-
Dichlorobenzidine. 3,3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/Vg-d)A-1
NA
NF
77E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E*00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
27E-01
NA
81E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA .
NA
NA
NA
NA
RAG
(mg/m3)
00525
NF
000225
00675
00875
00005
02625
0001S
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RIO
(mg/Vg-d)
1 5E-02
NF
6 4E-04
2 5E 02
2 5E 02
1 4E 04
7 5E 02
43E-04
10E+00
NA
NA
NA
NA
NA
NA
NA
NA
IDE -02
SOE-03
50E-03
SOE-03
3 BE -04
NA
7 IE 02
5 OE-02
7 1E-04
1 4E-04
15E-05
NF
1 OE-03
1 4E-03
5 OE-03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E 02
1 3E-02
1 3E-03
NA
64E04
NA
NA
50E 03
NA
5 7E 02
1 4E 0?
MA
NA
Emission
Rale
(g/sec)
67E-06
67E06
30E-04
2 9E-03
29E-04
20E-04
55E-06
15E-05
1 IE-OS
32E05
55E-06
55E-08
55E06
55E-06
55E-06
67E-06
1 3E-05
67E-06
37E05
10E-O4
55E-06
49E-04
67E-08
5 IE-OS
55E-06
89E-05
16E-04
55E-07
67E-06
67E-06
55E-06
37E-05
4 9E-04
2 7E 04
25E-04
67E06
55E06
67E06
55E-06
55E-06
55E06
55E 06
1 4E 04
55E06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
E2max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2max
E2 max
E2max
E2max
E2max
Elmax
E2max
E2max
E2max
E2max
E2 max
E2 max
E2 max
E2max
E2 max
E2m«
E2 max
E2 max
E2max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 ma»
E2 man
E2 mat
E2 ma«
E2 ma«
E2 man
E2 ma»
E2 man
Adult
Cancer
Risk
NT
NT
25E-11
NT
NT
52E-10
NT
47E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
23E-I3
NT
NT
NT
NT
NT
9 IE 11
78E-12
NT
NT
NT
1 1E-10
NT
23E-10
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
fit
NT
NT
NT
Child
Cancer
Risk
NT
NT
63E-11
NT
NT
1 3E-09
NT
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
40E-10
NT
NT
NT
58E-13
NT
NT
NT
NT
NT
2 3E-10
19E-11
NT
NT
NT
2 7E-10
NT
58E-10
42E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
W
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
38E-11
NT
NT
79E-10
NT
70E-12
NT
NT
NT
NT
NT
NT
NT
NT
24E-10
NT
NT
NT
35E-13
NT
NT
NT
NT
NT
1 4E-10
12E-11
NT
NT
NT
1 7E-10
NT
35E-10
2 5E-1 1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
W
NT
NT
Ml
MI
tJT
Farmer
Cancel
Risk
NT
NT
56E-11
NT
NT
1 2E-09
NT
10E-11
NT
NT
NT
NT
NT
NT
NT
NT
35E-10
NT
NT
NT
51E-13
NT
NT
NT
NT
NT
20E 10
1 7E-11
NT
NT
NT
24E-10
NT
52E-10
37E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
NT
NT
Nl
                                                                                                                                        Adult      Child   School-age   Farmer
                                                                                                                                      Noncancer Noncancer Noncancer Noncancer
                                                                                                                                         HQ       HQ       HQ       HQ
3 BE -08
NT
4 OE-05
98E-06
99E-07
1 2E-04
62E-09
29E-06
96E-10
NT
NT
NT
NT
NT
NT
NT
NT
57E-08
6 3E-07
1 8E-06
93E-08
12E-04
NT
61E-08
93E-09
1 IE-OS
94E«
31E-06
NT
5 7E-07
3 3E 07
62E-07
5 BE 08
90E-06
NT
28E-08
37E-07
NT
NT
3 7E 08
3 7E 08
3 7E-07
NT
7 3E-07
NT
NT
45E 07
NT
B2E 09
3 3E 08
NT
NT
1 4E-07
NT
1 5E 04
37E-05
37E-06
4 5E 04
2 3E-08
1 IE-OS
36E-09
NT
NT
NT
NT
NT
NT
NT
NT
2 1E-07
24E06
6 5E-06
35E-07
44E-04
NT
23E07
35E08
40E-OS
35E04
1 2E-05
NT
21E-06
12E-06
23E-06
2 2E 07
34E-OS
NT
1 1E-07
1 4E-06
NT
NT
1 4E 07
1 4E 07
1 4E 06
NT
2 7E 06
NT
NT
1 ?f. 06
MT
3 IE 08
1 ?f 07
m
111
8 6E-08
NT
9 OE-05
2 2E 05
2 2E-06
2 7E 04
1 4E-08
66E-06
22E-09
NT
NT
NT
NT
NT
NT
NT
NT
13E-07
14E-06
40E-08
2 1E-07
26E-04
NT
1 4E 07
2 IE-OS
24E-05
2 1E-04
70E06
NT
1 3E-06
74E07
1 4E-06
1 3E 07
2 OE-05
NT
6 4E 08
84E-07
NT
NT
84E 08
84E 08
84E 07
NT
1 6F_ 06
NT
NT
10F. 06
NT
1 BE 08
7 4E 08
NT
NT
3 8E-08
NT
4 OE-05
9 BE -06
9 9E-07
1 2E-04
62E-09
29E-06
96E-10
NT
NT
NT
NT
NT
NT
NT
NT
5 7E 08
6 3E-07
18E06
9 3E-08
1 2E-04
NT
81E-08
93E09
1 IE 05
94E05
31E-06
NT
5 7E-07
3 3E 07
6 2E-07
5 BE -08
90E-06
NT
2 BE 08
37E 07
NT
NT
37E08
3 7E 08
3 7E 07
NT
73E 07
NT
MT
45E 07
NT
82E09
33E 08
NT
NT
Volume V. Appendix V-14
-------
        (y QJ J



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-------
TABLE 14  Maximum Inhalation Risks and Noncancet HQs in Subarea E2
CHEMICAL
DichlorodWuoromelhane
Dlchloroelhane, 1,1- (Ethylidene dichlorlde)
Dichloroethane. 1.2-
Dichloroethene, 1.1- (Vinylidine chloride)
Dichloroethene (trans). 1 .2-
Dichloropheno). 2.4
Dichloropropane, 1,2- (Propylene dichlorlda)
Dfchloropropen* (els), 1 .3-
DtehioroproparM (trans). 1.3
Dretfylphthalate
Dimethoxybervcidine. 3,3'-
DimMhytphenol, 2.4-
Dimethylphthalale
CN-n-butylphthalata
CNnHrotoluwM. 2,6-
DinHro-2-melhylphenol. 4.6-
DmHrophanol. 2.4
DlnHrotoliMna, 2.4-
Dloxane. 1.4-
Di(n)octy) phthafate
D. 2,4-
Ethyl methacrytale
Etnytt«nzefM
Ettiy)*n« dibromide
Ethylene oxide
EBiylene thtourea
Fluoranthene
Fluor ana
Formaldehyde
Furfural
Heptachlor
HeptachloroWphenyl
Hexachtorobenzene
Hexachloroblphenyl
Hexachlorobutediene
Hexachtofocyclohexane, gamma (Llndana)
Hexachlorocyclopentadiene
Hexachloroethane
Hexachtorophene
Haxanona, 2-
lndeno( 1 ,2 ,3-cd)pyrene
Isophorone
Maleic hydrazlda
Methoxychlor
Methyl t-butyl ether
Methyl-2-Pentanone. 4- (MIBK)
Melhylene chloride
Methylnaphthalene, 2-
Monochlorobiphenyl
Naphthalene
Nitroanilme. 2-
Nitroaniline, 3-
Inhalation
Slope
Factor
(mg/kg-d)*-1
NA
NA
9 1E-02
1 2E«00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
16E+00
NA
78E-02
NA
NA
14E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF
RAC
(mg/m3)
005
0125
NA
0007875
00175
0002625
0001
0005
0005
0.7
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
0.0125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
0 75
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E-02
36E-02
NA
2 3E-03
5 OE-03
7 5E-04
29E-04
1 4E-03
1 4E-03
206-01
NA
506-03
NA
25E-02
25E-04
NF
50E-04
50E-04
NA
50E4J3
25E-03
23E42
7 1E-02
1 4E-05
NA
20E 05
10E-02
10EX)2
50E-02
3 6E-03
1 3E-04
NA
20E-04
NA
50E-05
75E-05
50E-06
25E-04
75E-05
NF
NA
50E-02
1 3E-01
1 3E 03
2 IE 01
5 7E 03
2 1E-01
NF
NA
1 OE02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E-04
3E-05
3E-05
3E05
3E-05
55E-06
3E-05
3E-05
3E-05
7E-05
2E-04
55E-06
55E06
16E-05
55E-06
55E-06
55E-06
55E-06
49E-04
55E-06
39E-05
2SE-04
50E04
1 2E-04
3 IE-OS
15E-10
S5E-06
67E-06
61E-04
55E06
5 5E-07
1 4E-08
55E-06
1 4E 08
1 OE 04
55E-05
55E-06
55E-06
32E-05
64E 05
55E-06
67E 06
1 2E-04
55E 07
1 3E 05
1 3E-05
40E-04
42E-05
1 7E-08
55E 06
67E 06
67E-06
Subarea
E2 max
E2 max
E2 max
E2 max
E2 max
E2max
E2max
E2max
E2max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2max
E2 max
E2max
E2 max
E2 max
E2mix
E2 max
E2 max
E2max
E2 max
E2max
E2 max
E2max
E2max
E2 max
E2max
E2 max
E2max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 ma
E2 ma
E2 ma
E2ma
E2 ma
E2ma
E2 ma
E2ma
£2 ma
E2ma
E2ma
Adult
Cancer
Risk
NT
NT
12E 11
1 6E-10
NT
NT
NT
1 8E-11
18E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
95E-10
1 2E-10
NT
NT
NT
30E-10
NT
27E-11
NT
97E-M
NT
86E-11
NT
NT
84E-13
NT
NT
NT
NT
NT
NT
NT
NT
7 IE 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
31E-11
4 1E-10
NT
NT
NT
44E 11
44E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
24E09
29E-10
NT
NT
NT
74E-10
NT
67E-11
NT
24E-10
NT
21E-10
NT
NT
21E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 8E 11
til
NT
m
NT
til
School-age
Cancer
Risk
NT
NT
19E-11
25E-10
NT
NT
NT
27E-11
27E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
14E-09
1 8E-10
NT
NT
NT
45E-10
NT
41E-11
NT
1 5E-10
NT
1 3E-10
NT
NT
1 3E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-11
(IT
NT
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
28E-11
36E-10
NT
NT
NT
39E-11
39E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
21E-09
2 6E-10
NT
NT
NT
66E-10
NT
60E-11
NT
2IE-10
NT
1 9E-10
NT
NT
1 9E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-11
NT
NT
NT
NT
NT
                                                                                                                                           Adult      Child   School-age  Farmer
                                                                                                                                         Noncancer Noncancer Noncancer Noncancer
                                                                                                                                            MQ       HQ       HO       HO
1 5E-06
30E-08
NT
47E-07
2 1E-07
6 2E-07
37E-06
74E-07
74E-07
72E-09
NT
9 3E-08
NT
53E-08
19E-06
NT
93E-07
93E-07
NT
93E-08
13E-06
92E-07
59E-07
68E-04
NT
62E-10
4 7E-08
5 7E-08
10E06
1 3E-07
37E-07
NT
23E-06
NT
1 7E 04
62E-05
93E-05
19E-06
36E-05
NT
NT
1 IE 08
7 8E-08
3 7E 08
50E 09
1 9E 07
1 6F. 07
NT
NT
4 7E 08
4 OF. 05
NT
54E-06
1 1E-07
NT
18E-06
79E-07
23E-06
1 4E-05
2 BE 06
28E-06
27EXJ8
NT
35E-07
NT
20E-07
70E-06
NT
35E06
35E-06
NT
35E-07
49E-06
35E-06
22E-06
2.6E-03
NT
23E-09
1.7E.-O7
2 1E-07
39E-06
49E-07
14E46
NT
6.7E-06
NT
64E-04
2 3E 04
3 SE-04
70E-06
1 4E-04
NT
NT
42E08
29E07
1 4E 07
1 9E 08
69E 07
59F. 07
NT
NT
1 7E 07
1 5F 04
rjT
33E-06
6 7E-08
NT
1 1E-06
4 BE -07
14E06
84E-06
17E06
1 7E-06
16E-08
NT
2 1E-07
NT
1 2E 07
42E-06
NT
21E-06
21E-06
NT
2 1E-07
30E-06
21E-06
3E06
5E-03
NT
4E09
1E-07
3E07
23E-06
30E07
8 4E-07
NT
53E-06
NT
39E04
1 4E 04
2 IE 04
42E 06
B2E-05
NT
NT
26E 08
1 BE 07
64E 08
1 IE 08
42E 07
35E 07
NT
HI
1 IE 07
90E-05
NT
1 SE-06
3 OE 08
NT
4 7E-07
2 1E-07
6 2E 07
37E-06
7 4E-07
7 4E-07
72E09
NT
9 3E-08
NT
5 3E 08
19E-06
NT
9 3E-07
93E-07
NT
9 3E 08
1 3E-06
92E-07
59E07
6 BE -04
NT
62E-10
4 7E-08
5 7E-08
1 OE 06
1 3E-07
3 7E-07
NT
23E-06
NT
1 7E-04
62E05
93E 05
19E06
36E-05
NT
NT
1 IE 08
7 BE 08
3 7E 08
50E 09
1 9E 07
1 BE 07
NT
NT
4 7E OB
40E-05
NT
Volume V. Appendix V-14
-------
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-------
TABLE 14  Maximum Inhalation Risks and Noncancer HQs in Subaiea E2
CHEMICAL
Nftroanillne. 4-
Nitrobenzene
Nibopheno). 2-
Nlbophenol. 4-
N-Nitroso-di-n-butylamlne
N Nitroso-dl-n-pfopylamln«
N-Nitrosodlphenytamlne (Diphenylamlne)
NonachtoroMphenyt
OctacMoroWphenyl
Pentachlorobenzena
Pentachlofoblphenyl
Pentachloronrtrobenzene
PentachkKOphenol
Phenanthren*
Phenol
Pyren*
Safrol*(5-{2-Propenyl)-t,3-benzodioxole)
Styren*
T «tr»chk>roblphenyl
Tetrachloroethane. 1,1.1.2-
Tetrachloroethane. 1,1.2,2-
Tetrachloroethen*
Tetrachtorophenol. 2,3.4.6-
Toluene
Trichloro-1,2,2-trttlunro«thane. 1.1.2-
Trichlorobenzene, 1 .2,4-
Trtchloroblphenyl
Trtchloroathane. 1.1,1- (Methyl chloroform)
Trlcnloroethane. 1.1,2-
Trichkxocthene
Trfchlorofluoromethane
Trtchlofophenol, 2.4.5-
Trichlotophenol. 2.4,6-
Vlnyl Metal*
Vinyl chloride
Xytene. m/p- (m/p-Oim»ttiyf benzene)
Xylene. o- (o-CMmelhyl bajizene)
2,3,7.8-TCDD
1.2.3.7,8-PCDO
1.2.3.4,7.8-HxCDO
1.2,3 6.7,8 HxCDO
1.2.3. 7.8,9 HxCDD
1. 2.3.4.6, 7.8-HpCDD
OCDD
2.3.7.MCDF
1.2,3,7.8-PCDF
2.3.4.7.8 PCDF
1.2.3.4.7. 8 HxCDF
1.2.3.6,7. 8 HxCDF
2,3.4,6.7.8-HxCDF
Inhalation
Slope
Factor
(mg/kg-d)A-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20EXJ3
NA
NA
NA
NA
NA
NA
5 7E 02
60E-03
NA
NA
1 OE 02
NA
30E-01
NA
NA
15E+05
7 5E+04
1 5E+04
1 5E+04
1 5E+04
1 5E»03
1 5E+02
1 5E+04
7 5E+03
7 5E+04
1 5E«04
1 5E»04
1 5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
002625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
175
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E4M
75E-03
NA
1 5E-Of
75E-03
NF
71E-02
NA
75E-03
NA
25E4J3
7 5E 03
29E-02
2 1E+00
1 4E-02
NA
71E-02
10E-03
NA
50E-02
25E-02
NA
1 4E-02
NA
50E-01
5 OE-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-08
67E-06
55E06
1 2E-04
67E-06
67E06
1 4E-08
1 4E-08
48E-05
1 4E-08
34E-05
55E06
67E-06
55E-06
55E06
1 2E-04
23E4*
1 4E-08
55E-06
55E-06
5 IE-OS
8 BE -08
61E-04
3 3E-04
55E-08
30E-08
1 3E-05
13E-05
19E-05
25E-04
55E-06
5SE-06
64E-05
2 5E-04
3 BE -04
55E-06
108E-11
678E-11
895E-11
I66E 10
1 09E-10
1 24E 09
6 15E 09
877E-11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
E2 max
E2max
E2 max
E2 max
E2max
E2 max
E2 max
E2max
E2 max
E2 max
E2max
E2 max
E2max
E2max
E2max
E2 max
E2 max
E2 max
E2max
E2 max
E2max
E2max
EZmax
E2max
E2max
E2 max
E2max
E2max
E2max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
E2 max
E2ma»
E2 max
£2 max
£2 ma*
E2 max
E2 max
E2 max
E2 ma»
Adult
Cancer
Risk
NT
NT
NT
NT
7 1E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-12
12E-11
1 1E-12
NT
NT
NT
NT
NT
NT
76E-12
12E-12
NT
NT
60E-13
NT
80E-10
NT
NT
1 BE-11
55E 11
1 5E-11
2 7E-11
1 BE 11
20E 11
1 OE-11
1 4E 11
28E-11
3 BE 10
23E 10
22E 10
25E 10
Child
Cancer
Risk
NT
NT
NT
NT
1 BE -08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 9E-12
3 OE-11
28E-12
NT
NT
NT
NT
NT
NT
t BE-11
30E-12
NT
NT
1 5E-12
NT
20E-09
NT
NT
44E-11
1 4E-10
37E-11.
68E-1!
44E It
5 IE 11
25E-1I
36E 11
70E 11
95E 10
58E 10
54E 10
6 IE 10
School-age
Cancer
Risk
NT
NT
NT
NT
1 IE-OB
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 3E-12
1 8E-11
t 7E-12
NT
NT
NT
NT
NT
NT
1 2E-11
1 8E-12
NT
NT
90E-13
NT
1 2E-09
NT
NT
27E-11
64E-11
22E 11
4 IE-It
2 7E 11
3 IE 11
1 5E 11
22E 11
42E 11
58E 10
35E 10
33E 10
37E 10
Farmer
Cancer
Risk
NT
NT
NT
NT
1 6E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
35E 12
27E-11
25E-I2
NT
NT
NT
NT
NT
NT
1 7E-I1
2 7E-12
NT
NT
1 3E-12
NT
1.8E-09
NT
NT
39E-11
12E-10
33E 11
60E 11
40E 11
45E It
22E 11
32E 11
63E 11
BSE 10
52E 10
49E 10
55E 10
                                                                                                                                           Adult     Child    School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HO       HQ       HQ
NT
33E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 BE -08
62E-08
NT
3 IE 09
8 2E-OB
NT
27E-08
NT
62E-08
NT
1 7E-06
7 7E 08
18E-06
13E-08
33E-08
NT
1 5E-08
1 IE-OS
NT
4 2E-07
19E-08
NT
38E-07
NT
65E-08
9 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
ur
NT
NT
NT
1 2E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
HE -05
23E-07
NT
1 2E-08
2 3E-07
NT
10E-07
NT
23E-07
NT
65E-06
2 9E 07
6 BE -08
4 9E-08
1.2E-07
NT
56E-08
40E-06
NT
16E46
7 OE-08
NT
14E-06
NT
2 4E-07
35E-09
NT
NT
NT
NT
m
NT
HI
NT
NT
NT
NT
NT
fJT
NT
74E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
B6E-06
14E-07
NT
70E09
1 4E-07
NT
6 OE-08
NT
1 4E-07
NT
39E08
1 7E 07
41E-06
3 OE-08
74E-08
NT
34E-08
24E-06
NT
9 4E-07
4 2E-08
NT
86E-07
NT
t 5E-07
2 1E-09
NT
NT
NT
NT
NT
(IT
NT
NT
NT
fIT
in
NT
NT
NT
33E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E06
62E-08
NT
3 IE 09
62E-08
NT
27E-08
NT
62E-08
NT
17E06
77E-08
1BE-06
1 3E-08
33E 08
NT
15E-08
1 IE 08
NT
4 2E-07
1 9E-08
NT
3 BE -07
NT
65E-08
93E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
MT
NT
Volume V. Appendix V-14
-------
TABLE  ', 4  Maximum Inhalation Risks and r4oncancer HQs in Subaica E2
CHEMICAL
1. 2.3.7.8.9 HxC OF
1.2.3.4.6.7 8 HpC OF
1.2.3,4. 7,8.9 HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivalant)
Copper
Lead
Mercury (and MoHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
^articulate matter
^esplrable particulars
Inhalation
Slope
Factor
(mg/kg-d)"-1
1 5E»04
1 5E»03
1 5E»03
\ 5E*02

NA
NA
50
NA
64
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E-05
36E-05
1 3E-03
1 3E-04
13E-03
2 5E-01
NA
NA
21E05
50E-03
1 3E-03
1 3E 03
1 8E 05
7 5E-02
50E 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E 09
1 22E 09
1 89E-08
4 28E-08
24E-04
42E-06
37E-05
1 5E 04
33E08
16E-05
7 1E-07
7 1E-07
94E-05
43E-05
1 4E-03
50E-08
4 7E-04
1 5E-05
34E-05
1 2E-04
32E-02
24E»00
91E-02
7 2E-02
7 2E-02
Subarea
E2 max
E2 max
E2 max
E2 max

E2 max
E2 max
E2max
E2max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2 max
E2max
E2max
E2 max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2 max
Oft-sile
Vapor
Cone
(ug/m3)
91E 11
29E 09
38E-10
59E-09

74E-05
1 3E-06
1 IE-OS
47E05
1 OE-08
50E06
2 2E-07
2 2E 07
29E-05
1 3E 05
4 3E 04
1 6E 06
1 SE-04
47E-06
1 1E-05
3 7E-05
9 9E-03
75E-01
2 8E-02
2 2E-02
2 2E-02
Cancer
Adult
Dose
(mg/kgd)
32E-15
1 OE-13
1 3E-14
2 IE 13
4 7E-13
26E-09
46E-11
40E-10
16E-09
36E-13
1 7E 10
77E-12
77E-12
1 OE-09
47E-10
1 5E-08
55E-11
51E-09
1 6E-10
37E-10
1 3E-09
35E^)7
26E-05
99E-07
7 9E 07
7 9E-07
Cancer
Child
Dose
(mg/kg d)
80E 15
25E 13
33E 14
52E 13
1 2E-12
65E-09
1 1E-10
1 OE 09
4 1E-09
90E 13
44E 10
1 9E-11
1 9E-11
26E-09
1 2E-09
38E-08
1 4E-10
1 3E-08
4 1E-10
92E 10
33E 09
8 7E 07
66E-05
25E-06
20E-06
20E-06
Cancer
School age
Dose
(mg/kg-d)
48E-15
1 5E 13
20E-14
3 1E-13
70E-13
39E09
69E-11
6 IE 10
25E09
54E-13
26E-10
1 2E 11
12E-11
1 5E-09
71E-10
2 3E-08
82E-11
77E-09
25E-10
56E-10
2 OE-09
53E-07
40E-05
1 5E 06
1 2EO6
1 2E-06
Cancer
Farmer
Dose
(mg/kg d)
7 IE 15
23E 13
30E 14
46E 13
1 OE-12
58E09
1 OE-10
90E-10
36E09
80E 13
39E-10
1 7E-11
1 7E-11
23E-09
1 OE 09
34E08
1 2E-10
1 1E-08
36E 10
82E-10
29E09
7 BE -07
59E 05
22E-06
1 7E 06
1 7E-06
Noncancer
Adull
Dose
(mg/kgd)
25E-14
79E 13
1 OE 13
16E 12
36E 12
20E08
36E 10
3 IE 09
1 3E48
28E-12
1 4E«9
60E 11
80E 11
8 OE-09
37E09
1 2E-07
42E 10
4 OE-08
1 3E-09
29E09
10EO8
27E06
2 1E-04.
77EO6
6 1E-06
6 IE 06
Noncancer
Child
Dose
(mg/kg-d)
93E 14
30E 12
39E 13
60E-12
1 4E 11
7 6E 08
1 3E-09
1 2E 08
4 8E 08
10E 11
51E-09
23E-10
23E10
3 OE-08
1 4E-08
4 4E 07
1 6E 09
1 5E 07
4 BE 09
1 1E 08
3 BE 08
10EJB
7 7E 04
29E05
23E05
23E-05
Noncancer
School-age
Dose
(mg/kgd)
56E 14
1 8E 12
23E 13
36E-12
82E 12
46E-08
81E-10
71E-09
29E-08
63E-12
31E-09
1 4E-10
1 4E-10
1 8E-08
B2E-09
27E-07
96E 10
90E08
29Efl9
6SE-09
23E-08
61E-06
4 6E 04
1 7E-05
1 4E 05
1 4E05
Noncancer
Farmer
Dose
(mg/kgd)
25E-14
79E-13
1 OE-13
16E-12
36E-12
2 OE-08
36E-10
31E-09
1 3E-08
28E-12
14E-09
60E 11
60E 11
80E09
37E-09
1 2E^)7
42E-10
40E-OB
1 3E09
29E09
1 OE-08
27E08
2 1E 04
77E-06
6 1E46
6 IE 06
  NA - Not applicable
  NF-Not found
  NT " No toxkrty informarjon
  HQ " Hazard quotient   '
  HI -Hazardindex
 olums V. Appendix V 14
-------
                  V
                       i
TABLE 14  Maxtmum Innaiation Risks and Noncancet HQs in Subarea E2
CHEMICAL
1.2.37.8,9-HxCDF
1.2.3,4.6,7,8-HpCDF
1.2,3.4,7.8,9-HpCDF
OCDF
Dloxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MaHg)
Nickel
Salanlum
Slrvef
Thallium
Zinc
Hydrogan chlorlda
Total nHrogan oxides (NOx)
Total sulfur oxldas (SOx)
Particuteta matter
Resplrable particulates
Inhalation
Slop*
Factor
(mg/kg-d)»-1
1 5E+04
1 5E*03
1 5E+03
1 5E+02

MA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
3 BE -05
1 3E-03
13E-04
1 3E-03
25E-01
NA
NA
2 IE-OS
50E-03
1 3E-03
1 3E-03
18E4)5
75E-02
50E-04
NA
NA
NA
NF
Emission
Rata
(a/sac)
293E-10
9 30E-09
1 22E 09
1 69E-08
4 28E-08
, 24E04
42E-06
37E-05
15E4M
33E-08
16E-OS
71E-07
71E-07
94E-05
43E45
14E-03
50E-08
47E-04
15E-05
34E-05
12E-04
32E-02
24E+00
91E-02
72E-02
72E-02
Subarea
E2max
E2 max
E2 max
E2 max

E2max
E2max
E2max
E2max
E2max
E2max
E2 max
E2max
E2 max
E2 max
E2 max
E2 max
E2max
E2 max
E2max
E2m*x
E2 max
E2 max
E2 max
E2max
E2 max
Adult
Cancer
Risk
48E-11
1 5E-10
20E-11
31E-11
1 5E-09
NT
NT
206-06
NT
30E-12
1 1E-09
32E-10
NT
NT
NT
NT
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
1 2E-10
38E-10
50E 11
77E-11
3 8E-09
NT
NT
50E-08
NT
75E-12
27E09
79E-10
NT
NT
NT
NT
1 1E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
72E-11
23E-10
30E-11
47E-11
23E-09
NT
NT
30E-08
NT
46E-12
16E-09
48E-10
NT
NT
NT
NT
69E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
1 1E-10
34E-10
44E-11
69E 11
34E-09
NT
NT
45E-08
NT
67E-12
24E-09
7.1E-10
NT
NT
NT
NT
10E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NOTES:
  NA - Not applicable
  NF - Not found       v
  NT • No toxlctty Information
  HQ • Hazard quotient
  HI -HazardIndex
                                                                              Total Risk   34E-08    65E-08    5 1E-08    76E-08
                                                                                                                                            Adult      Child    School-age  Farmer
                                                                                                                                          Noncancer Noncancer Noncancer Noncancer
                                                                                                                                             HQ       HQ       HQ       HQ
NT
NT
NT
NT
NT
NT
36E-O6
42E-05
36E-04
22E-09
1 1E-05
4 8E-08
2 4E-10
NT
NT
5 5E-03
85E08
32E-05
IDE -06
1 6E-04
1 4E-07
5 4E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E-05
1 6E-04
1 3E 03
84E-09
4 IE-OS
1 8E-07
90E-10
NT
NT
2 1E 02
3 2E-07
1 2E 04
36E-06
6 2E 04
5 1E-07
20E02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
8 IE 06
95E-05
61E-04
51E4W
25E05
1 1E-07
54E-10
NT
NT
1 3E 02
19E07
72E05
23E-06
37E04
31E-07
1 2E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E06
42E-05
3 6E 04
22E49
1 1E05
4 BE 08
2 4E-10
NT
NT
55E03
6 5E-08
32E-05
10E-08
16E^)4
14E^)7
5 4E-03
NT
NT
NT
NT
                                                                                                                                  Total HI   I3E-02   49E-02   30E-02   1 3E-02
/oluma V. Appendix V-14
-------
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-------
TABLE 15  Maximum Inhalation Risks and Noncancef HQs In Subatea E3
CHEMICAL
Acenaphthene
Acenaphthytene
Acetaldehyde
Acetone
Acetophenone
ActytonHrile
Anthracene
Benzene
Benzole acid
Benzotrlchloride
Benzo(a)antfiracene
Benzo(a)pyrene
Benzo(b)fluoranro*thoxy) methane
Bfe(2-chtoro«lhyt)efher
Bls(2-«hlorolsopropyl)ether
Bli(2-«thy1hexyl)phthBlata
Bromodtchlofometh«n«
Bromoform
Bromomethane
Bromodlphenyf ether, p-
Butonone. 2- (Methyl ethyl ketone)
Butylbenrylphlhalate
Carbon dlsulflde
Carbon tetrachlortde
Chtordane
Chtoro-3-me«ny)phenol. 4-
Chtoroaniline, p- (4-ChloroanHlne)
Chlorobenzene
Chlorobenztlate
Chloroethane (Ethyl chloride)
Chloroform
ChtoronwHiane
Chtoronaphthalene, beta
Chlorophenol, 2- v
Chlorodiphenyl ether, 4-
Chrysene
Cresol. m-
Cresol, o- (2-MethytphenoQ
Cresol. p-
Crotonaldehyde
Cumene
DDE. 4.4'-
Dibenz(a.h)anthracene
Dibfomochiofomsthane
Dichlorobenzene. 1 .3-
Dlchlorobenzene, 1,4-
Dlchlorobenzene. 1,2-
Dichlorobeiuidine. 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)*-1
NA
NF
77E-03
NA
NA
24E-01
NA
296-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
2 7E-01
NA
8 IE 02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
0262S
ooots
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
2.5
000875
NA
0.07
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
15E-02
NF
6 4E-04
2 5E-02
2 5E-02
1 4E-04
7 5E-02
43E-04
1 OEtOO
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E-03
50E-03
50E-03
36E-04
NA
7 IE 02
SOE-02
7 1E-04
1 4E-04
15E-05
NF
10E-03
1 4E-03
5 OE-03
71E-01
25E-03
NA
20E-02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
6 4E-04
NA
NA
5 OE-03
NA
5 7E-02
1 4E 02
NA
NA
Emission
Bate
(B/sec)
67E-06
67E-06
30E-04
29E-03
29E-04
20E-04
55E-06
, t 5E-05
IIE^M
32E-05
55E-06
55E06
55E06
55E-06
55E-08
67E-06
t 3E-05
87E-06
37E-05
tOE-04
S5E-06
49E-04
87E4>e
51E-O5
55E-06
89E-05
16E-04
55E-07
87E^W
67E-06
55E-06
37E-05
49E-04
27E-04
2 5E-04
67E-06
55E-06
87E-06
55E06
55E-06
55E-06
55E06
1 4E-04
55E 06
55E 07
55E 06
26E05
55E06
55E06
55E 06
33E 05
4 7E 08
Subarea
E3 max
E3max
E3max
£3 max
E3max
E3max
E3max
E3max
E3max
E3max
E3m«x
ESmax
E3mex
E3max
E3max
E3max
E3max
E3max
ESmax
ESmax
E3max
E3max
E3max
ESmax
ESmax
ESmax
ESmax
ESmax
E3max
ESmax
E3 max
ESmax
£3 max
ESmax
ESmax
ESmax
ESmax
ESmax
ESmax
E3max
ESmax
E3max
ESmax
E3ma»
E3max
E3 max
E3max
E3 max
E3max
E3 max
E3max
E3 max
Adult
Cancer
Risk
NT
NT
75E-12
NT
NT
1 6E-10
NT
14E-12
NT
NT
NT
NT
NT
NT
NT
NT
47E-I1
NT
NT
NT
69E-14
NT
NT
NT
NT
NT
27E-11
23E-12
NT
NT
NT
33E-11
NT
69E-11
50E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
19E-11
NT
NT
3 9E-tO
NT
34E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-10
NT
NT
NT
1 7E-13
NT
NT
NT
NT
NT
67E-11
57E-12
NT
NT
NT
81E-11
NT
1 7E-10
12E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
1 1E-11
NT
NT
23E-10
NT
21E-12
NT
NT
NT
NT
NT
NT
NT
NT
71E-M
NT
NT
NT
10E-13
NT
NT
NT
NT
NT
416-11
35E-12
NT
NT
NT
49E-11
NT
1 OE-10
75E-12
NT
NT
NT
NT
NT
NT
NT
NT
MF
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
1 7E-11
NT
NT
35E-10
NT
31E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
15E-13
NT
NT
NT
NT
NT
60E-11
51E-12
NT
NT
NT
72E-11
NT
1 5E-10
1 IE-It
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                          Adult      Child   School-age   Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HQ        HO       HQ
1 1E-08
NT
1 2E-05
29E06
30E-07
36E-05
1 8E-09
87E-07
2 8E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-OB
19E^)7
52E^)7
2 BE -08
35E-05
NT
1 8E-08
28E-09
31E09
28E-05
9 2E-07
NT
17E-07
97E-08
19E-07
1 7E-08
27E-06
NT
84E49
1 1E-07
NT
NT
1 IE-OS
1 IE-OS
1 1E-07
NT
22E-07
NT
NT
t 3E 07
NT
24E 09
97E 09
NT
NT
42E-08
NT
44E-05
1 1E 05
1 1E-06
1 3E-04
69E-09
32E-06
1.1E-09
NT
NT
NT
NT
NT
NT
NT
NT
83E-08
7 OE-07
19E08
1 OE-07
13E-04
NT
6 BE 08
10E48
t2E-05
10E04
35E-06
NT
6 3E-07
36E07
69E-07
65E08
10E05
NT
3 IE 08
4 1E-07
NT
NT
4 IE 08
4 IE 08
4 IE 07
NT
8 IE 07
NT
ra
50E 07
NT
9 IE 09
36E 08
NT
NT
2 5E-08
NT
2 7E-05
66E-06
6 7E 07
80E-05
42E-09
20E-06
64E-10
NT
NT
NT
NT
NT
NT
NT
NT
3 BE 08
4 2E-07
12E-06
6 3E-08
78E-05
NT
4 1E-08
63E-09
71E-06
83E05
21E-06
NT
3 BE -07
2 2E-07
4 2E 07
39E-08
61E-06
NT
1 9E-06
2 5E 07
NT
NT
25E 08
25E 08
2 5E 07
NT
49E07
NT
NT
3 OE-07
NT
55E09
2 ?E 08
NT
NT
1 1E-08
NT
1 2E 05
29E-06
30E07
3 6E 05
1BE-09
87E-07
2 8E-10
NT
NT
NT
NT
NT
NT
NT
NT
17E48
1 9E-07
52E^>7
2 BE -08
35E-OS
NT
16E48
2 BE -09
3IEP6
2 BE -05
92E-07
NT
1 7E-07
97E-08
1 9E 07
17E08
27E06
NT
64E09
1 1E-07
NT
NT
1 IE 08
1 IE 08
1 1E-07
NT
2 2E-07
NT
NT
1 3E 07
NT
24E 09
9 7F. 09
NT
NT
Volume V, Appendix V 14
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TABLE 15  Maximum Inhalation Risks and Noncancei HQs in Subarea E3
CHEMICAL
Dlchtofodifluorom»tn»ne
Dichtoroethane, 1.1- (Ethylidene dichloride)
Dichtoroethana, 1.2-
Dlchloroethane. 1,1- (Vlnylidina chloride)
Dlchloroethene (trans). 1.2-
Oichlofophanol. 2.4-
DichkHopropane. 1,2- (Piopylane dichlorlda)
Dkhkxopfopene (els), 1.3-
DIchloraprofMna (trans). 1 .3-
DtotfiylphttMlate
Dlmelhoxybarwldlne. 3.3'-
Dlm«lhytpb«nol. 2,4-
Dlmelhylphthalate
Dl n-butylprilhalate
CHnttrotoliMne. 2.6-
CHnltio-2-methylphenol, 4.6-
Dlnttrophanol. 2.4-
CMnKrotoluene. 2,4-
Dtoxane. 1.4-
Dl(n)octyl phthalate
D.2.4-
Ethyt methacrylite
Ettiyluanzane
Ethylena dtbromtde
Ethylene oxlda
Elhylene thtoure*
Fluoranthene
Fluorana
Formaldehyde
Furfural
Haptechlbr
HaptecnlofOvlpiianyl
Haxachlorobanzene
Hexachloroblphenyl
HaxachkKobutadlana
HaxKhtorocyclohexana. gamma (Llndana)
Hexachlorocyclopentadleria
H*xachloro«thana
Haxachtorophana
Hexanone, 2-
lnd«no(1 ,2,3-ed)pyrene
Isophoron*
Malaic hydrazida
Methoxychlor
M«ttiyl-t butyl ather
Melhyl-2-Pentanone, 4- (MIBK)
Mettiytene chloride
Methylnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nitroaniline. 2-
NitToanilina. 3-
Inhalation
Slop*
Factor
(mg/kg-d)*-1
NA
NA
91E-02
1 2E+00
NA
NA
NA
1.3E-01
1.3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
35E-01
NA
NA
NA
45E-02
NA
4SE+00
NA
16E+00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA " '
NA
NF
RAC
(mg/m3)
005
0125
NA
0007875
00175
0 002625
0001
0005
0005
0.7
NA
00175
NA
00875
0000675
NF
000175
000175
NA
00175
000675
0 07875
025
000005
NA
000007
0035
0035
0175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0 004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E-02
3 6E-02
NA
23E-03
50E-03
75E-04
29E-04
1 4E-03
14E-03
20E-01
NA
50E-03
NA
25E-02
25E-04
NF
50E-04
50E-04
NA
SOE-03
25E-03
23E42
7 1E-02
1 4E-05
NA
20EOS
10E02
10E -O2
50E-02
3 6E-03
13E-04
NA
20E-04
NA
50E05
75E-05
50E-06
25E04
75E-05
NF
NA
50E-02
1 3E-OI
1 3E-03
2 1E-01
5 7E 03
2 1E-OI
NF
NA
10E 02
1 4E-05
NF
Emission
Rate
(g'sec)
2 5E-04
3E-05
3E-05
3E-05
3E-05
5E-C6
3E-05
. 3E-05
3E-05
7E-05
2E-04
55E-00
55E-06
1 6E-05
55E-06
55E-06
SSE-06
55E-06
49E-04
55E4J6
39E-05
25E-04
50E-04
1 2E-04
3 IE-OS
15E-10
55E46
67E-06
61E-04
55E-06
S5E^>7
1 4E-08
55E-06
1 4E-06
10E04
55EXW
55E-06
55E06
32E-05
64E-05
55E-06
67E-06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E06
6 7E 06
6 7E 06
Subarea
E3max
E3max
E3 max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
ESmax
E3max
E3max
E3max
E3max
£3 max
E3max
E3 max
E3max
E3 max
E3max
E3max
E3max
E3m»x
ESmax
E3max
E3 max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3max
E3 max
E3max
E3 max
E3 max
E3 max
E3max
E3 man
E3 max
E3 max
E3 max
E3 max
E3 max
Adult
Cancer
Risk
NT
NT
37E-12
49E-11
NT
NT
NT
52E-12
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E 10
35E-11
NT
NT
NT
8 8E-1 1
NT
80E-12
NT
29E-11
NT
2 6E-1 1
NT
NT
25E-13
NT
NT
NT
NT
NT
NT
NT
NT
2 IE 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
92E-12
1 2E-10
NT
NT
NT
1 3E-11
1 3E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
71E-10
86E-11
NT
NT
NT
22E-10
NT
20E-11
NT
71E-11
NT
64E-11
NT
NT
62E-13
NT
NT
NT
NT
NT
NT
NT
NT
53E 12
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
55E-12
73E-11
NT
NT
NT
79E-12
79E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
43E-10
52E-11
NT
NT
NT
1 3E-10
NT
1 2E-11
NT
43E-11
NT
3 8E-1 1
NT
NT
38E-13
NT
NT
NT
NT
NT
NT
NT
NT
32E 12
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
82E-12
1 1E-10
NT
NT
NT
12E-11
12E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
63E-10
77E-11
NT
NT
NT
20E-10
NT
1.8E-11
NT
64E-11
NT
57E-11
NT
NT
55E-13
NT
NT
NT
NT
NT
NT
NT
NT
4 7E 12
NT
NT
tIT
NT
m
                                                                                                                                            Adult      Child   School-age   Farmer
                                                                                                                                         Noncancer Noncancer Noncancar Noncancer
                                                                                                                                            HQ       HQ       HQ       HQ
4 3E-07
8 BE -09
NT
1 4E-07
6 3E-08
1 8E-07
1 1E-06
22E-07
22E-07
21E-09
NT
2 BE -08
NT
16E08
55E-07
NT
2 6E-07
2 BE -07
NT
2 BE 08
39E-07
27E-07
18E-07
20E-04
NT
18E-10
1 4E-08
1 7E-08
3 1E-07
39E08
1 1E-07
NT
89E-07
NT
5 IE-OS
18E-05
2 BE 05
5 5E 07
11E-05
NT
NT
34E09
23E-08
1 IE 08
1 5E 09
55E 08
4 7E 08
NT
NT
1 4E 08
1 2E 05
NT
1 6E 06
3 3E-08
NT
5 2E-07
24E-07
69E-07
41E-06
8 2E 07
8 2E-07
79E-09
NT
10E-07
NT
59E08
21E-06
NT
10E-06
10E-06
NT
10E-07
15E4)6
IDE -06
66E-07
76E^4
NT
69E-10
S2E48
63E-08
1 1E-06
14E4)7
4 1E-07
NT
26E46
NT
19E-04
69E-05
1 OE 04
2 IE 06
4 OE 05
NT
NT
1 3E 08
8 7E 08
4 IE 08
55E 09
2 IE 07
1 7E-07
NT
NT
52E 08
44E 05
NT
9 8E-07
2 OE-08
NT
3 2E 07
14E-07
4 2E-07
25E06
50E07
50E-07
4 BE -09
NT
63E-OB
NT
3 6E 08
1 3E-06
NT
6 3E-07
63E-07
NT
63E-08
88E07
62E-07
4 OE 07
46E-04
NT
42E-10
3 IE-OB
3 BE 08
69E07
B BE 06
2 5E-07
NT
16E-06
NT
1 1E-04
42E 05
6 3E-05
1 3E 06
24E-05
NT
NT
76E 09
52EOB
25E 08
33E 09
1 ?E 07
1 IE 07
NT
NT
3 IE 08
2 7E-05
NT
4 3E-07
8 BE -09
NT
1 4E-07
63E-08
1 8E-07
1.1E-06
2 2E-07
2 2E 07
21E-09
NT
2 BE -08
NT
1 6E-08
55E-07
NT
2 8E-07
28E-07
NT
2 BE -08
39E4)7
27E-07
1 BE 07
20E-04
NT
t 8E 10
1 4E-08
17EflB
31E-07
39EOB
1 1E-07
NT
6 9E-07
NT
5 IE-OS
1 BE -05
2 BE 05
55E07
1 IE-OS
NT
NT
34E09
23E08
1 IE 08
15E 09
55E 08
4 ?E-08
NT
NT
1 4E 08
1 2E 05
NT
Volume V. Appendix V-14
-------
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                 V   j
TABLE 15  Maximum Innalalion Risks and Noncancer HQs in Subarea E3
CHEMICAL
Nitroanllin*. 4-
Nitrobenzene
Nibophenoi. 2-
Nibophenol. 4-
N Nitroso-di-n-butylamine
N-Nrtroso-di-n-propylamine
N-Nrb-osodlphanyiamlne (Dtphenytamine)
NonachkNobtphanyl
Octachtoroblphenyl
Pentachkxobenzene
Pantachtoroblphanyl
PantachloronHrobanzene
Pantachkxophanol
Phenanlhrene
Phanol
Pyrana
Safrola (5-(2-PropenyT)-1 ,3-benzodioxole)
Slyrana
Tetrachloroblphenyl
Tetrachtoroethane. 1.1.1.2-
Talrachloroathana. 1,1,2,2-
Tetrachloroethana
Tebachlorophenol. 2.3.4.6-
TohMna
Tr1chioro-t.2.2-bitluefoerhane. 1.1.2-
Trichlorobenzana, 1 ,2,4-
Trichlotobiphanyl
Trichtofoalhana, 1,1.1- (Methyl chloroform)
Trichloroathana. 1,1,2-
Trichloroattiena
Trlchioroftuoromethane
Trichlorophanol. 2.4.5-
Trichlorophenol. 2.4.6-
Vlnyl acetate
Vinyl chloride
Xylana, m/p- (m/p-Dimethyl banzana)
Xylana, o- (o-Dimelhyl banzana)
2,3,7.8-TCDD
1,2.3.7,8-PCDD
1,2.3,4,7.8-HxCDD
1.2.3.6,7.^HxCDO
1. 2.3.7.8.9 HxCDD
1.2.3,4.6.7.8-HpCDD
OCDD
2.3,7.8-TCDF
1.2.3,7.8-PCDF
2.3.4.7.8-PCDF
1 2 3 4.7.8-HxCDF
1 '2 3,6.7.8 HxCDF
2.3.4.6.7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)*-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
10E-02
NA
30E-01
NA
NA
15E+05
756*04
1 5E+04
1 5E+04
1 5E+04
1 5E*03
1 5E+02
1 5E»04
75E+03.
7 5E»04
1 5E+04
1 5E»04
1 5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0.525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
75E-03
NF
71E-02
NA
75E-03
NA
25E-03
75E-03
29E-02
21E»00
1 4E-02
NA
71E-02
1 OE-03
NA
50E-02
25E-02
NA
1 4E-02
NA
5 OE-01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
tJA
HA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E06
55E 06
1 2E-04
67E-06
67E-06
1 4E-08
1 4E-06
48E-05
14E-08
34E-05
55E-06
67E-06
55E-08
55E-06
1 2E4M
23E4W
1 4E-08
55E-06
55E-08
51E-05
6 BE ^6
61E-04
33E-04
55E-06
30E-08
1 3E-05
1 3E-05
19E-05
25E-04
55E-06
55E-06
64E-05
25E-04
3 BE -04
55E06
1 08E-11
678E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
877E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
E3max
E3 max
E3max
E3max
E3max
E3max
E3max
E3max
ESmax
E3max
E3max
ESmax
E3max
E3max
E3max
E3max
E3max
E3mtx
E3max
E3max
E3max
ESmax
E3mix
E3max
E3max
E3max
E3max
E3max
E3max
E3mix
E3max
E3max
E3mix
E3 mix
E3max
E3 max
E3max
E3max
E3max
E3max
E3max
E3ma
E3ma
E3ma
E3ma
E3ma
E3ma
E3ma
E3 ma
E3ma
Adult
Cancer
Risk
NT
NT
NT
NT
2 1E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
46E-13
36E-12
34E-13
NT
NT
NT
NT
NT
NT
23E-12
36E-13
NT
NT
18E-13
NT
24E-10
NT
NT
52E 12
1 6E 11
43E 12
BOE 12
53E 12
60E 12
30E 12
4 3E 12
B4E 12
1 IE 10
69E 11
65E 11
73E 11
Child
Cancer
Risk
NT
NT
NT
NT
53E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-12
90E12
84E-13
NT
NT
NT
NT
NT
NT
57E-12
90E-13
NT
NT
44E-13
NT
59E-10
NT
NT
1 3E 11
4 IE 11
1 IE 11
20E 11
1 3E 11
1 5E 11
74E 12
1 IE 11
2 IE 11
2 BE 10
1 7E 10
1 6E 10
1 BE 10
School-age
Cancer
Risk
NT
NT
NT
NT
32E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
69E-13
54E-12
5 IE-IS
NT
NT
NT
NT
NT
NT
35E 12
54E-13
NT
NT
2 7E-13
NT
36E-10
NT
NT
79E 12
25E 11
65E-12
1 2E 11
80E 12
9 IE 12
45E 12
64E 12
1 3E 11
1 7E 10
1 OE 10
9 BE 11
t IE 10
Farmer
Cancer
Risk
NT
NT
NT
NT
4 7E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
10E-12
80E-12
75E-13
NT
NT
NT
NT
NT
NT
5 IE 12
80E-13
NT
NT
40E-13
NT
53E-10
NT
NT
1 2E-11
37E 11
97E 12
1 BE 11
1 2E 11
1 3E 11
66E 12
95E 12
1 9E 11
25E 10
1 5E 10
1 IE 10
1 6E 10
                                                                                                                                            Adult      Child   School-age   Farmer
                                                                                                                                          Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                             HQ        HQ        HQ       HQ
NT
9 7E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-06
1 8E-08
NT
92E-10
18E-08
NT
79E-09
NT
1BE-O8
NT
52E-07
23E48
54E-07
39E-09
97E^9
NT
44E-09
31E-07
NT
1 2E-07
55E-09
NT
1 1E-07
NT
19E-08
26E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HI
NT
36E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
42E06
69E-08
NT
35E-09
69E-08
NT
30E-08
NT
69E-08
NT
1964)6
856 -08
20E-O6
14E48
36E-08
NT
16E-OB
1 2E-08
NT
4 6E 07
2 1E-08
NT
4 2E-07
NT
7 2E 08
IDE -09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
tJT
NT
22E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E-06
4 2E-08
NT
2 IE 09
42E-08
NT
1 BE-OB
NT
42E-08
NT
12E06
S2E-08
12E-06
8 BE 09
22E^»
NT
1 OE 08
71E-07
NT
2 BE 07
1 3E 08
NT
26E-07
NT
43E08
B3E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
9 7E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 08
18E-08
NT
92E-10
18E-08
NT
79E09
NT
1BE-08
NT
52E-07
23E08
5 4E 07
39E-P9
97E-09
NT
44E09
31E-07
NT
1 2E-07
55E-09
NT
1 1E-07
NT
19E-08
2 BE- 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
 k/olume V. Appendix V-14
-------
TABLE IS  Maximum Inhalation Risks and Noncancei HQs in Subarea E3
CHEMICAL
1.2 3.7.8,9 HxCDF
1.2.3 4,6.7.8 HpCDF
1. 2.3,4. 7.8.9-HpCDF
OCOF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mtrcury (ano MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Partculate matter
Resplrable partlculales
Inhalation
Slope
Factor
(mg/kg d)*-1
1 5E*04
1 5E«03
1 5E»03
1 5E«02

NA
MA
50
NA
84
61
41
NA
NA
NA
NA
OB4
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
i oe 04
75E-05
36E 05
1 3E 03
1 3E 04
1 3E-03
25E 01
NA
NA
2 IE 05
50E03
1 3E 03
1 3E 03
1 BE 05
75E 02
50E-04
NA
NA
NA
NF
Emission
Rale
(g/sec)
2 93E 10
930E 09
1 22E 09
1 89E 08
428E 08
2 4E-04
• 4 2E-06
37E-05
1 5E-04
33E-08
16E-05
7 1E-07
7 IE 07
94E 05
43E05
1 4E 03
50EOB
4 7E 04
1 5E 05
34E 05
1 2E 04
32E02
24E«00
9 1E 02
72E 02
7 2E 02
Subarea
E3 max
E3 max
E3 max
E3 max

E3 max
E3max
E3max
E3 max
E3max
E3max
E3 max
E3max
E3max
E3 max
E3 max
E3max
E3 max
E3 max
£3 max
E3 max
E3max
E3 max
E3max
E3max
E3 max
Off sits
Vapor
Cone
(ug/m3)
2 7E 11
86E-10
1 IE 10
1 7E-09

22EOS
39E 07
34E-06
1 4E 05
30E 09
15E-06
6 5E-08
6 5E-08
86E 06
40E 06
1 3E-04
46E-07
43E05
1 4E 06
3 IE 06
1 1E-05
29E-03
22E-01
84E03
66E 03
66E 03
Cancer
Adult
Dose
(mg/kg-d)
95E 16
30E t4
40E 15
6 IE 14
1 4E 13
7 BE 10
1 4E 11
1 2E 10
49E-10
1 1E-13
52E-11
23E-12
23E 12
30E 10
1 4E 10
45E-09
16E-11
15E09
49E 11
1 1E-10
39E-10
1 OE-07
7 BE 06
2 9E 07
2 3E 07
2 3E 07
Cancel
Child
Dose
(mg/kg d)
2 4E 15
75E 14
99E 15
1 5E 13
35E-13
1 9E 09
34E-11
30E 10
1 2E-09
2 7E 13
1 3E-10
57E-12
57E 12
76E 10
35E-10
1 IE 08
40E-11
38E09
1 2E 10
2 7E-10
97E-10
? 6E 07
20E-05
73E07
5 BE 07
5 8E-07
Cancer
School-age
Dose
(mg/kg d)
1 4E-15
45E 14
60E 15
92E 14
2 1E-13
12E09
20E 11
1 6E-10
73E-IO
16E 13
78E-11
35E-12
35E-12
46E 10
2 IE 10
68E-09
24E-11
23E09
73E 11
17E-10
59E-10
t 6E-07
1 2E 05
44E07
35E07
35E-07
Cancer
Farmer
Dose
(mg/kg-d)
2 1E-15
67E 14
8 BE 15
1 4E 13
3 IE 13
1 7E 09
30E 11
2 7E-10
1 1E-09
24E-13
1 2E-10
51E-12
5 1E-12
66E-10
3 1E-10
10E-08
36E-11
34E-09
1 IE 10
2 4E-10
86E 10
2 3E-07
1 7E 05
66E07
52E07
5 2E-07
Noncancei
Adult
Dose
(mg/kg d)
74E 15
23E 13
3 IE 14
48E 13
1 IE 12
60E09
1 IE 10
93E 10
3 BE 09
83E-13
40E-10
18E-11
18E It
24E09
1 IE 09
35E 08
1 3E 10
1 2E-08
3 BE 10
86E 10
30E-09
8 IE 07
6 IE 05
23E 06
1 BE 06
1 BE 06
Noncancer
Child
Dose
(mg/kg-d)
28E-14
88E 13
1 IE- 13
1 BE 12
40E-12
2 3E 08
40E-10
35E-09
1 4E-08
3 1E-12
15E-09
67E-11
67E-11
88E-09
40E-09
1 3E-07
4 7E-10
44E-08
1 4E 09
32E09
1 1E-08
30E-06
23E-04
86E06
6 BE 06
68E 06
Noncancer
School-age
Dose
(mg/kgd)
1 7E 14
53E 13
69E 14
1 1E 12
24E-12
1 4E 08
24E 10
21E-09
8 5E-09
1 9E-12
91E-10
40E-11
40E 11
53E-09
24E49
80E08
2 BE 10
27E-08
65E 10
19E-09
68E 09
1 BE 06
1 4E 04
52E06
4 IE 06
4 IE 06
Noncancer
Farmer
Dose
(mg/kg d)
74E 15
23E 13
3 IE 14
48E-13
1 IE 12
60E 09
1 IE 10
93E 10
3 BE 09
83E 13
40E 10
18E 11
1 BE 11
24E-09
1 IE 09
35E08
1 3E 10
1 2E 08
3 BE 10
86E-10
30E-09
B IE 07
6 IE-OS
23E 06
1 8E06
1 BE -06
NOTES
  NA - Not applicable
  NF * Not found
  NT " No toxicHy Information
  HO * Hazard quotient
  HI -HazardIndex
 'olume V. Appendix V-14
-------
TABLE 15  Maximum lrii._..»tion Risks and Noncancer HQs in Subaiea E3
CHEMICAL
1,2.3.7,8.9-HxCDF
1.2,3.4,6.7.8-HpCDF
1,2.3.47.8,9-HpCDF
OCDF
Dtoxfn TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivatont)
Copper
lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Tctal nitrogen oxides (NOx)
Total sulfur oxides (SOx)
ParHculate matter
Resplrable parttculates
Inhalation
Slope
Factor
(mg/kg-d)M
1 5E+04
1 5E+03
1 5E+03
1 5E+02

NA
MA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000081
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
IDE -04
75E^>5
36E-05
13E-03
1 3E-04
13E43
25E-01
NA
NA
2 IE-OS
50E03
1 3EX»3
13E^)3
1 8E-05
75E-02
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E-09
1 89E-08
428E-08
24E-04
, 42E-06
37E-05
15E-04
33E08
16E-05
7 1E 07
71E-07
94E-05
43E05
1 4E-03
50E-06
47E-04
15E05
34E-05
1 2E-04
32E^>2
24E+00
91E-02
72E-02
72E-02
Subatea
E3max
E3max
E3 max
E3 max

E3max
E3max
E3max
E3max
E3max
E3max
£3 max
E3max
E3max
E3max
E3max
E3max
E3 max
E3max
E3max
E3 max
E3max
E3max
E3max
E3max
E3max
Adult
Cancer
Risk
14E-11
45E-11
59E 12
92E-12
46E-10
NT
NT
60E-09
NT
90E-13
3 2E-10
94E-11
NT
NT
NT
NT
1 4E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
35E-11
1 1E-10
1 5E-11
23E-11
1 1E-09
NT
NT
15E-08
NT
2 2E-12
79E-10
23E-10
NT
NT
NT
NT
34E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School- age
Cancer
Risk
2 1E-11
68E-11
69E-12
14E-11
69E-10
NT
NT
90E-09
NT
1 4E-12
4 8E-10
1 4E-10
NT
NT
NT
NT
20E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
32E-11
1 OE-10
1 3E-11
20E-11
1 OE-09
NT
NT
1 3E-08
NT
20E-12
7 OE-10
21E-10
NT
NT
NT
NT
30E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NOTES:
  NA»No» applicable
  NF-Not found      ':
  NT • No toxlctty Information
  HQ • Hazard quotient
  HI -Hazardindex
                                                                               Total Risk   1 OE-08    2 5E-08    1 5E-08    2 2E-08
                                                                                                                                            Adult     Child    School-age  Farmer
                                                                                                                                          Noncancer Noncancer Noncancei Noncancer
                                                                                                                                             HQ       HQ       HQ       HQ
NT
NT
NT
NT
NT
NT
11E-06
1 2E-05
1 1E-04
67E-10
32E-08
1 4E-08
72E-11
NT
NT
1 6E-03
2 5E-08
95E06
30E-07
49E05
40E-08
16E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
40E-08
4 6E-05
40E-04
25E-09
12E-05
53E-08
2.7E-10
NT
NT
8 2E-03
94E-08
35E-05
1 1E-06
1 BE 04
1 5E-07
80E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
24E06
2.6E-05
2 4E04
15E-09
73E-06
3 2E-08
1 6E-10
NT
NT
37E-03
57E08
2 IE-OS
6.8E-07
1 1E-04
9.1E-08
36E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-OB
12E05
1 1E-04
8 7E-10
32E06
14E08
72E-11
NT
NT
16E-03
25E08
95E-06
30E-07
49E05
40E-08
1 6E-03
NT
NT
NT
NT
                                                                                                                                  Total HI    39E-03    1.5E-02    88E-03   39E-03
Volume V. Appendix V-14
-------
TABLE 16  Maximum Inhalation Risks and Noncancei HQs in Subaica N1
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrylonrtnle
Anthracene
Benzene
Benzole acid
Benzotr (chloride
Benzo(a)anthracene
Benzo(a)pyr»ne
Benzo(b)fluoranmene
Benzo(g,h.l)perylene
Benzo(k)f1uoranthene
Bls(2-ehloroethoxy) methane
Bls(2 chloroethyl)ether
8l](2-chlorolsopropyl)ether
8rs(2-ethylhexyt)phthalate
Bromodichloromethane
Bromoform
Bromomelhane
Bromodiphenyl ether, p-
Butanone. 2- (Methyl ethyl ketone)
Butylbenzyfphthalale
Carbon disurfide
Carbon tetrachlorlde
Chlordane
Chloro-3-m«lhy1phenol. 4-
Chloroaniline, p- (4-Chloroaniline)
Chlorobenzane
Chlorobvnzilate
Chloroethane (Ethyl chloride)
Chloroform
Chloromethan*
Chloronaphthalen*. beta
^hlorophenol, 2-
rhlorodiphenyl ether. 4-
;hrysene >;
;resol. m-
;resol. o- (2-Methylphenol)
;resoi, p-
;rolonaldehyde
:umene
)DE.4,4-
)ibenz(a h)anthracene
)ibromochloromettiane
)ichlorobenzene. 1.3
lichlorobenzene, 1.4-
lichloroberurene, 1,2-
lichloroberuridme. 3.3'-
lichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)"-
NA
NF
7 7E 03
NA
NA
24E-01
NA
29E 02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E 02
1 3E»00
NF
NA
NA
2 7E-01
NA
8 IE 02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA'
NA
NA
RAC
1 (mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000075
NA
007
0 004375
NF
NA
004375
004375
0004375
NA
000275
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/Vg-d)
1 5E-02
NF
6 4E 04
25E 02
2 5E 02
1 4E 04
75E 02
4 3E-04
1 OE*00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
5 OE 03
50E 03
50E 03
36E 04
NA
7 1E-02
50E 02
7 IE 04
1 4E 04
1 5E-05
NF
1 OE 03
1 4E 03
50E 03
7 IE 01
2 5E-03
NA
20E 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
64E 04
NA
NA
50E 03
NA
5 7E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E 06
6 7E 06
3 OE 04
29E 03
2 96 04
20E 04
55E-06
1 5E 05
. 1 IE-OS
32E 05
55E06
55E-06
55E06
55E 06
55E 06
67E 06
1 3E-05
6 7E 06
3 7E-O5
1 OE-04
55E-06
49E-04
67E 06
5 IE 05
55E 06
89E 05
1 6E 04
5 5E 07
67E 06
67E 06
55E 06
3 7E 05
49E 04
2 7E 04
2 5E 04
67E 06
55E 06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Off site
Vapor
Cone
Subaiea (ug/m3)
N1 max 25E06
N1 max 2 5E 06
N1 max 1 1E 04
N1 max 1 IE 03
N1 max 1 1E 04
Nt max 7 7E 05
N1 max 2 IE 06
N1 max 56E06
N1 max 4 3E-06
N1 max 1 2E-05
N1 max 2 1E 06
N1 max 2 1E-06
Nt max 2 1E-06
N1 max 2 IE 06
N1 max 2 1E-06
N1 max 25E06
Nt max 5 IE 06
N1 max 25E-06
Nt max 1 4E^>5
N1 max 3 9E-05
N1 max 2 1E-06
N1 max 1 9E 04
N1 max 2 5E-06
N1 max 20E 05
N1 max 2 IE 06
N1 max 3 4E 05
Ntmax 60E05
N1 max 2 IE 07
N1 max 2 5EX)6
N1 max 2 5E 06
N1 max 2 IE 06
N1 max 1 4E 05
N1 max 1 9E-04
N1 max 1 OE 04
N1 max 9 3E-05
N1 max 25E-06
Ntmax 2 IE 06
N1 ma
N1 ma
N1 ma
Nt ma
N1 ma
Nt ma
m ma
rn ma
rn ma
rn ma
rn ma
N1 ma
N1 ma
rn ma
rn ma
25E 06
2 IE 06
2 IE 06
2 IE 06
2 IE 06
53E 05
2 IE 06
2 1E 07
2 IE 06
1 OE 05
2 IE 06
2 IE 06
2 1E 06
1 3E 05
1 BE 08
Cancer
Adult
Dose
(mg/kg-d)
90E 11
90E 11
40E 09
39E 08
39E 09
2 7E 09
74E 11
20E 10
1 5E 10
43E 10
74E-11
74E 11
74E-11
74E 11
74E 11
90E 11
1 BE 10
90E-11
50E-10
1 4E 09
74E-11
66E-09
90E-11
69E-10
74E-11
1 2E 09
2 1E 09
74E 12
90E 11
90E-11
74E-11
49E-10
66E-09
3 6E-09
3 3E-09
90E-11
74E 11
90E 11
74E 11
74E-11
74E 11
74E 11
1 9E 09
74E 11
74E 12
7 4E 11
35E 10
7 4E It
74E 11
74E 11
45E 10
63E 13
Cancer
Child
Dose
(mg/kg-d)
22E 10
22E 10
1 OE 08
97E 08
9 BE 09
67E 09
1 8E 10
49E 10
3BE-10
1 1E 09
1 8E-10
1 BE 10
1 8E-10
1 BE 10
18E 10
22E 10
44E 10
22E 10
1 2E 09
34E09
1 8E-10
1 6E 08
22E 10
1 7E-09
1 8E-10
30E 09
53E 09
1 BE 11
22E 10
22E-10
1 8E-10
1 2E-09
1 6E-08
89E09
8 2E-09
22E-10
1 BE 10
22E-10
1 8E-10
1 8E 10
1 8E-10
1 BE 10
46E 09
1 8E 10
1 8E 11
1 8E 10
8 BE 10
1 BE 10
1 BE 10
1 BE 10
1 IE 09
1 6E 1?
Cancer
School-age
Dose
mg/kg d)
1 3E 10
1 3E 10
6 1E 09
58E-08
59E 09
4 1E 09
1 1E-10
30E-10
23E 10
64E-10
1E-10
IE 10
1E 10
IE 10
IE 10
3E 10
2 7E 10
1 3E-10
75E-10
2 1E-09
1 1E-10
99E-09
3E-10
OE 09
1E-10
BE 09
32E-09
1E-11
3E-10
3E-10
1E-10
74E-10
9 9E-09
54E-09
49E-09
1 3E-10
1 1E-10
1 3E 10
1 IE 10
1 IE 10
1 IE 10
1 IE 10
78E 09
1 IE 10
1 IE 11
1 IE 10
53E 10
1 IE 10
1 IE 10
1 IE 10
6 7E 10
94F H
Cancer
Farmer
Dose
(mg/kg-d)
20E-10
20E 10
89E09
8 7E 09
1 6E-10
44E-10
34E-10
95E 10
1 6E 10
1 6E-10
1 6E 10
1 6E-10
1 6E-10
20E 10
40E 10
20E-10

3 1E-09
1 6E-10
1 5E4)8
20E 10
1 5E 09
1 6E-10
2 7E-09
4 7E-09
1 6E-11
20E 10
20E-10
1 6E-10
1 1E-09
1 5E 08
79E09
7 3E-09
20E 10
16E 10
20E 10
1 6E-10
1 6E 10
1 6E 10
1 6E-10
4 IE 09
1 6E 10
1 6E 11
1 6E 10
7 BE 10
1 6E 10
1 6E 10
1 6E 10
99F 10
1 IF 1?
Noncancer
Adult
Dose
(mg/kg d)
70E-10
70E 10
3 IE 08
30E 07
30E 08
2 IE 08
57E 10
1 5E 09
1 2E 09
33E09
57E 10
57E 10
57E 10
57E-10
57E-10
70E 10
1 4E 09
70E 10
3 9E 09
t IE 08
57E 10
5 1E-08
70E 10
54E 09
57E-10
93E09
1 6E-08
5 7E 11
70E 10
70E 10
57E 10
3 BE 09
5 IE 08
2 8E 08
2 5E 08
70E 10
57E-10
70E-10
57E-10
57E 10
57E 10
57E 10
1 4E 08
57E 10
5 7E 11
5 7E 10
2 7E 09
5 7E 10
5 7C 10
5 7F 10
3 5f 09
4 9f 17
Noncancer
Child
Dose
(mg/kg-d)
26E 09
26E 09
1 2E 07
1 IE 06
1 IE 07
7 9E-08
21E09
5 7E 09
44E09
1 2E 08
2 1E 09
2 IE 09
2 1E-09
2 IE 09
2 1E-09
26E 09
52E09
26E 09
1 4E 08
40E 08
2 1E 09
1 9E^)7
26E-09
2 OE 08
2 IE 09
35E 08
6 2E 08
2 1E-10
26E 09
26E 09
2 IE 09
1 4E 08
1 9E 07
10E 07
95E 08
26E 09
2 IE 09
26E 09
2 IE 09
2 1E 09
2 IE 09
2 1E 09
54E 08
2 IE 09
2 IF 10
2 IF. 09
1 or os
2 IE 09
2 IE 09
7 1E 09
1 3E 08
1 BF 11
Noncancer
School age
Dose
(mg/kg d)
1 6E 09
1 6E 09
7 IE 08
6 BE 07
6 9E 08
4 7E 08
1 3E 09
35E09
27E09
75E 09
1 3E 09
1 3E 09
1 3E 09
1 3E 09
1 3E-09
1 6E 09
3 1E-09
1 6E-09
87E 09
2 4E 08
1 3E 09
1 2E 07
1 6E 09
1 2E 08
1 3E 09
2 IE 08
3 7E 08
1 3E 10
1 6E 09
1 6E 09
1 3E 09
86E 09
1 2E 07
63E 08
58E 08
1 6E 09
1 3E 09
1 6E 09
1 3E 09
1 3E 09
1 3E 09
1 3E 09
33E 08
1 3E 09
1 3E 10
1 3E 09
6 2E 09
1 3E 09
1 3E 09
1 3E 09
7 BE 09
1 1F 11
Noncancer
Farmer
Dose
(mg/kgd)
70E-10
70E 10
3 IE 08
30E07
30E 08
2 IE 08
57E 10
1 5E 09
12E 09
33E09
57E 10
57E 10
57E 10
57E 10
5 7E-10
70E 10
1 4E-09
70E-10
39E-09
1 1E-08
57E-10
5 1E-08
70E-10
54E-09
5 7E-10
93E-09
1 6E-08
5 7E-11
70E-10
70E 10
5 7E 10
3 BE 09
5 1E-08
2 8E-08
2 5E-08
70E-10
5 7E-10
70E-10
57E 10
5 7E-10
5 7E 10
5 7E 10
1 4E 08
5 7E 10
5 7E 11
5 7E 10
2 7E 09
5 7E 10
5 7E 10
5 7E 10
3 5E 09
4 <)F 17
ofume V. Append" V 14
-------
TABLE 16  Maximum Inhalation Risks and Noncancel HQs in Subarea N1
CHEMICAL
Acenaphthene
Acenaphthylene
AcetaWehyde
Acetone
Acetophenone
Acrytonltrile
Anthracene
Benzene
Benzole acid
Beraotrtchtoride
Benzo(a)anthracen»
Benzojajpyrene
Benzo(b)fluoranlh*ne
Benzo(g.h,f)perylene
Benzo(l()fluoranthene
Bls(2-chloroethoxy) methane
Bls(2-chlofoethyl)ether
Bis(2-chlorolsopropyl)ether
Bls(2-ethythexyl)phlhala)e
Btomodlchloromethane
Bromoform
Bromomethane
Bromodlphenyl ether, p-
Butanone. 2- (Methyl ethyl ketone)
Butylbenrylphth.lale
Carbon dlsulfide
Carbon totrachloride
Chlordane
Chloro-3-methytphenol. 4-
Chloroanlllne, p- (4-CMoroaniline)
Chlorobenzene
Chlorobenzilate
Chbroethane (Ethyl chloride)
Chloroform
Cn1ororfwtha.no
Chloronaphthalene. beta
Chlorophenol, 2- -.
Chlorodlphenylefher, 4-
Chrysene
Cresol, m-
Cresol, o- (2-Methytphenol)
Crasol, p-
Crotonaldehyde
Cumene
DDE. 4, 4'-
Dib«nz(a.h)anthracene
Dibromochloromethane
Dichlorobenzene, 1.3-
Dichlorobenzene, 1 ,4-
Oichlorobenzene. 1,2-
Dichlorobenzidine. 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)"-1
MA
NF
77E-03
NA
MA
24E41
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E*00
NF
NA
NA
27E-01
NA
81E42
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA'
NA
NA
RAC
(mo'm3)
00525
NF
000225
00675
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
0.0035
0005
00175
25
000875
NA
007
0 004375
NF
NA
0 04375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
15E-02
NF
64E-04
25E42
25E-02
1 4E-04
75E-02
43E-04
1 OE+00
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E-03
50E-03
50E-03
36E-04
NA
7 IE 02
50E^)2
71E-04
1 4E-04
15E-05
NF
10E-03
1 4E-03
50E-03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E-02
1 3E-02
1 3E 03
NA
6 4E-04
NA
NA
50E-03
NA
5 7E-02
1 4E 02
NA
NA
Emission
Rate
(y/sec)
87E-08
87E-08
30E-04
2 9E-03
29E-04
20E-04
55E-08
. 15E-05
11E-05
32E-05
55E-06
55E-08
55E06
55E06
55E-06
67E-08
1 3E-D5
87E-06
37E-05
IDE -04
S5E06
49E-04
67E-06
5 IE-OS
S5E-06
89E-05
t 6E-04
55E-07
67E-08
B7E-06
55E-06
37E-05
4 9E-04
2 7E-04
2 5E-04
67E 06
55E-06
67E-06
55E-06
55E06
55E-06
55E-06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nt max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nt max
N1 max
N1 max
N1 max
Ntmax
N1 max
Nt max
N1 max
Nl ma*
N1 max
Nl max
Ml max
Nl ma.
Nl man
Nl max
Nl man
Nl ma«
Adult
Cancer
Risk
NT
NT
316-11
NT
NT
64E-10
NT
57E-12
NT
NT
NT
NT
NT
NT
NT
NT
20E-10
NT
NT
NT
28E-13
NT
NT
NT
NT
NT
1 1E-10
9SE-12
NT
NT
NT
1 3E-10
NT
29E-10
21E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
77E-11
NT
NT
16E-09
NT
1 4E-11
NT
NT
NT
NT
NT
NT
NT
NT
49E-10
NT
NT
NT
71E-13
NT
NT
NT
NT
NT
2 6E-10
24E-11
NT
NT
NT
33E-10
NT
71E-10
51E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
tn
NT
Nt
NT
NT
School-age
Cancer
Risk
NT
NT
47E-11
NT
NT
97E-10
NT
86E-12
NT
NT
NT
NT
NT
NT
NT
NT
29E-10
NT
NT
NT
43E-13
NT
NT
NT
NT
NT
1 7E-10
1 4E-11
NT
NT
NT
20E-10
NT
43E-10
31E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
m
NT
W
NT
m
Farmer
Cancer
Risk
NT
NT
69E-11
NT
NT
1 4E-09
NT
1 3E-11
NT
NT
NT
NT
NT
NT
NT
NT
4 4E-10
NT
NT
NT
63E-13
NT
NT
NT
NT
NT
2 5E-10
2 1E-11
NT
NT
NT
30E-10
NT
6 4E-10
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
tir
NT
NT
NT
NT
W
NT
                                                                                                                                           Adult     Child   School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HO       HO       HQ
46E-08
NT
4 9E-05
1 2E-05
12E-06
1 5E-04
76E-09
36E-06
1.2E-09
NT
NT
NT
NT
NT
NT
NT
NT
70E-08
7 7E-07
2 IE 06
1E-07
4E-04
NT
5E08
1E48
3E-05
2E-04
38E-06
NT
70E4J7
4 OE-07
7 7E-07
7 IE 08
11E-05
NT
35E-08
46E-07
NT
NT
4 6E 08
4 6E-08
46E07
NT
8 9E-07
NT
NT
55E07
Mr
1 OE 08
4 Of. OS
NT
NT
1 7E-07
NT
18E-04
45E-05
46E06
55E-04
29E-08
1 3E-05
44E-09
NT
NT
NT
NT
NT
NT
NT
NT
2 6E-07
29E-06
80E-06
4 3E-07
53E-04
NT
2 BE -07
43E-08
49E05
43E-04
14E-OS
NT
26E-08
15E-06
29E06
2 7E-07
4 IE-OS
NT
1 3E-07
1 7E-06
NT
NT
1 7E 07
1 7E 07
1 7E 06
NT
33E06
NT
NT
20E 06
NT
3 7E 08
1 5f 07
NT
111
1 OE-07
NT
1 1E-04
27E-05
2 BE -06
3 3E-04
17E-08
61E06
27E-09
NT
NT
NT
NT
NT
NT
NT
NT
16E-07
17E-06
4 BE -06
26E47
32E-O4
NT
1 7E-07
26E-08
29E-05
26E-04
86E-06
NT
16E-06
9 OE-07
17E06
1 6E-07
25E-05
NT
79E-06
10E-06
NT
NT
1 OE 07
1 OE 07
10E 06
NT
20E-06
NT
NT
1 2E 06
NT
23E 08
90E 08
NT
NT
46E-08
NT
49E-05
1 2E 05
12E-06
1 5E 04
7 BE -09
36E06
1.2E-09
NT
NT
NT
NT
NT
NT
NT
NT
7 OE 08
7 7E-07
21E-06
1 IE 07
1 4E-04
NT
7 5E-08
1 IE-OB
1 3E 35
1 2E 04
3 BE -06
NT
7 OE-07
40E07
7 7E 07
7 1E 08
1 1E 05
NT
35E06
46E-07
NT
NT
46E08
4 6E 08
4 6E-07
NT
8 9E-07
NT
NT
55E 07
Nf
1 OE 08
40E 08
NT
fIT
Volume V. Appendix V-14
-------
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TABLE 16  MaximumV   ^ion Risks and Noncancer HQs in Subatea N1
CHEMICAL
Dichlorodrfluoromelhane
Dichloroethane, 1.1- (Ethylidena dichlotide)
DlchlOfoettiane. 1 ,2-
Dtchtefoelhene. 1,1- (Vinylidine chloride)
Dichtoroettiene (trans), 1 ,2-
Dtchtefophenol. 2.4-
CHchkxopropane. 1 ,2- (Propylene dlchloride)
Dtehtoropfopene (crs). 1 .3
Dtchkxoptopene (trans). 1 ,3-
Dfethylpnlnalate
Omvthoxybenztdlne, 3.3"-
Dimethytphenot. 2.4-
Dtm«thytphthalale
Dl-n-butylphthalate
DlnNrotoluene. 2.6-
Dlnttro-2-nMthylphenol, 4.6-
Dtnrbophenol. 2,4-
CNnKrotohrane. 2.4-
Dtoxane. 1.4-
CM(n)oetyl phlhalata
0,2.4-
Ethyl methacrylate
Ethylbenzene
Elhyten* dibfotnlde
Ethylene oxide
Ethyton* thlourea
Fhioranthene
Fluotene
Formaldehyde
Furfural
Haptechior
Heptachlorobiphenyl
Hexachlorobenzene
Hexachloroblphenyl
Hexachlorobutadlen*
Hexachlorocyclohexane, gamma (LIndane)
Hexachlorocyclopentadiene
Hexachtofoethane v
Hexachlorophene
Hexanone, 2-
lndeno( t ,2.3-cd)pyrene
Isophorone
Malete hydrazlde
Melhoxychlor
Melhyl-l-birtyl ether
Methyl-2-Pentanone. 4 (MIBK)
Methylene chloride
Methylnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nitioaniline. 2-
Nrtfoanilme. 3-
Inhalation
Slope
Factor
(mg/kg-d)A-1
NA
NA
91E-02
12E+00
NA
NA
NA
13E41
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E-01
3 5E-01
NA
NA
NA
456-02
NA
45E+00
NA
16E+00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E -03
NF .
NA
NA
NA
NF
RAC
(mg/m3)
005
0125
NA
0007675
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00675
0000875
NF
000175
000175
NA
00175
000875
0 07675
025
000005
NA
000007
0035
0035
0 175
00125
0000436
NA
00007
NA
0000175
0000263
0000016
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RID
(mg/Vg-d)
1 4E-02
3 6E-02
NA
2 3E-03
SOE-03
75E-04
2 9E-04
1 4E-03
1 4E-03
20E-01
NA
SOE-03
NA
2SE-02
2SE-04
NF
5 OE 04
50E-04
NA
50E-03
25E-03
2 3E 02
7 1E-02
1 4E-05
NA
20E-05
10E-02
1 OE-02
50E-02
3 6E-03
1 3E 04
NA
20E-04
NA
50E05
75E-05
50E06
25E-04
75E-05
NF
NA
50E02
1 3E 01
1 3E 03
2 IE 01
57E 03
2 IE 01
MF
NA
1 OE 02
1 4E 05
NF
Emission
Rale
(g/sec)
25E-04
3E-05
3E-05
3E-05
3E-05
55E-06
3E-05
3E-05
• 3E-05
7E-05
2E-04
55E-08
55E-06
16E-05
55E-06
55E-06
55E06
55E-08
49E-04
55E-06
39E4»
25E04
50E-04
1 2E-04
3 IE-OS
1 5E-10
55E-06
87E-06
81E-04
55E-06
5 5E-07
1 4E-08
55E-06
HE 08
10E-04
55E-05
55E-06
55E06
32E05
64E05
55E 06
67E 06
1 2E 04
55E07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E-06
Subarea
N1 max
Nt max
N1 max
Nt max
N1 max
Nt max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nlmax
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
N1 max
Nlmax
N1 max
Nlmax
Nlmax
Nt max
N1 max
Nt max
N1 max
Nt max
N1 max
Ntmax
N1 max
Nl max
N1 max
Nl max
Nt max
Nt mat
Nl mai
Nl m *
Ml m •
Nl m ,
Ml m •
Ml m i
Ml ma.
Ml mat
Ml ma*
Adult
Cancer
Risk
NT
NT
15E-11
20E-10
NT
NT
NT
22E-11
22E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
12E-09
1 4E-10
NT
NT
NT
3 7E-10
NT
33E-11
NT
1 2E-10
NT
1 1E-10
NT
NT
10E-12
NT
NT
NT
NT
MT
NT
MT
MT
8 7E 12
MT
Mr
MT
MT
MT
Child
Cancer
Risk
NT
NT
38E-11
50E-10
NT
NT
NT
54E-11
54E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
29E09
36E-10
NT
NT
NT
91E-10
NT
82E-11
NT
30E-10
NT
26E-10
NT
NT
26E 12
NT
NT
NT
NT
NT
NT
MT
MT
?2E M
Ml
fJI
MT
MT
MT
School-age
Cancer
Risk
NT
NT
23E-11
30E-10
NT
NT
NT
33E-11
33E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
18E-09
22E-10
NT
NT
NT
S5E-10
NT
50E-11
NT
1 6E-10
NT
16E-10
NT
NT
16E-12
NT
NT
NT
NT
NT
NT
fJT
tJT
1 3E 11
fIT
tJT
MT
MT
MT
Farmer
Cancer
Risk
NT
NT
34E-11
45E-10
NT
NT
NT
48E-11
48E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E-09
32E-10
NT
NT
NT
8 1E-10
NT
74E-M
NT
26E-10
NT
23E-10
NT
NT
23E-12
NT
NT
NT
NT
NT
MT
MT
MT
1 9E II
MT
MT
MT
MT
MT
                                                                                                                                          Adult     Child   School-age   Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                          HQ       HQ       HQ       HO
1 BE -06
3 6E-08
NT
5 BE -07
2 6E-07
76E-07
46E-06
91E-07
91E07
B8E-09
NT
1 1E-07
NT
65E08
23E-08
NT
IE 06
1E-06
NT
1E-07
6E-06
1E-06
3E-07
84E-04
NT
7 6E-10
5 7E-C8
70E-08
13E06
1 6E-07
4 6E-07
NT
29E-06
NT
21E-04
76E-05
1 IE 04
23E06
44E-05
NT
NT
1 4E-08
96E 08
46E08
6 IE 09
23E 07
1 9E 07
MT
MT
57E 08
49F 05
fJT
67E-06
1 4E-07
NT
22E-06
9 7E-07
29E-06
17E-05
34E-06
34E-06
33E-08
NT
43E4>7
NT
2 4E 07
86E-06
NT
43E-06
43E-06
NT
43E-07
60E06
42E06
27E4)6
31E-03
NT
2 BE -09
2 1E 07
2 6E-07
47E-06
60E-07
t 7E-06
NT
1 IE-OS
NT
79E-04
2 8E-04
4 3E-04
66E06
1 7E-04
NT
NT
52E 08
36E 07
1 7E 07
23E 08
85E 07
72E 07
MT
MT
2 IE 07
1 BE 04
MT
40E-06
B2EOB
NT
13E-06
59E07
1 7E-06
10E-05
21E-06
2 IE 06
20E-08
NT
26E-07
NT
1 5E4)7
S2E-06
NT
26E-06
26E-08
NT
2 BE -07
36E-06
26E46
6E-06
9E-03
NT
7E-09
3E07
BE -07
29E-06
3 6E-07
10E-06
NT
65E-06
NT
4 7E 04
1 7E 04
26E04
52E06
1 OE 04
NT
NT
3 IE 08
22E 07
1 OE 07
1 4E 08
5 IE 07
4 3F 07
MT
MT
1 3E 07
1 IE 04
MT
1 8E-06
36E-08
NT
5 BE 07
2 6E-07
76E-07
46E-06
91E-07
9 IE 07
88E-09
NT
1 1E-07
NT
65E-08
23E-08
NT
1E-06
.1E-06
NT
1E-07
6E06
1E-06
7 3E-07
64E-04
NT
76E-10
S 7E 08
70E06
1 3E 06
1 6E 07
46E-07
NT
29E-06
NT
2 1E-04
7 6E 05
1 1E-04
23E06
44E-05
NT
NT
1 4E 08
9SE 08
46E 08
6 IE 09
23E 07
1 9E 07
MT
MT
57E 08
49E 05
MT
Volume V. Appendix V-14
-------
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TABLE 16  Maximumv    jlion Risks and Noncancer HQs in Subarea N1
CHEMICAL
Nilroanlline. 4-
Nitiobenzene
Nitrophenol. 2-
Nltrophenol. 4-
N Nttroso-dl n-butylamlne
N-NKroso-dl-n-propylamlne
N-Nttrosodfphenylamlne (Diphenylamlne)
Nonachloroblphenyl
OctachloroWphenyt
Pentacniorooenzane
Pentachkxobiphenyl
Pentachkxonttrobenzene
Pentachtofopnenol
Phenanthrene
Phenol
Pyrene
Safiole (5-(2-Propenyf)-t.3-benxodioxole)
Styrene
Tebachloroblphenyl
Tebachtoroethane. 1.1.1,2-
Telrachforoethane. 1.1,2,2-
Tetrachloroethene
Tebachtorophenol. 2,3.4.6-
Toluene
Tricnloto-1,2.2-«rHluoroethane. 1,1.2-
Trichlorobenzene, 1.2.4-
TrlchtoroWphenyl
Trkhlofoethane. 1.1.1- (Methyl chloroform)
Trlchloroethane. 1.1. 2-
Trichloroethene
Trkhlorofluoromethane
Trtchtorophenol. 2,4,5-
Trtchlorophenol. 2.4,6-
Vlnyl acetate
Vinyl chloride
Xytene, m/p- (m/p-Dlmethyl benzene)
Xylene. o- (o-Dlmethyt benzene)
2,3.7.8-TCDD
1. 2.3,7.8- PCDD
1,2,3.4,7.8-HxCDD
1.2.3.6.7.8-HxCDO
1.2.3.7.8.9-HxCDD
1,2.3.4,6,7,8-HpCDD
OCDD
2.3.7.6-TCDF
1.2.3.7,8-PCDF
2,3,4.7.8-PCDF
1,2.3.4.7.8 HxCDF
1.2,3.6.7.8 HxCDF
2,3.4,6.7.8-HxCDF
Inhalation
Slope
Factor
(mg/kg-d)*- 1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
80E-03
NA
NA
10E-02
NA
30E-01
NA
NA
15E+05
7 5E+04
1 5E*04
1 5E+04
15E*04
1 5E*03
1 5E»02
1 5E*04
7 5E+03
75E»04
15E+04
1 5E»04
1 5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0.175
00875
NA
005
NA
175
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
75E-03
NF
71E-02
NA
75E-03
NA
2 5E-03
75E-03
29E-02
21E+00
1 4E-02
NA
71E02
IDE -03
NA
50E-02
2SE-02
NA
1 4E-02
NA
50E-01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E 06
67E-06
55E-06
1 2E-04
67E-06
67E06
1 4E-08
' 14E-08
48E-05
ME 08
34E-05
55E-06
87E06
55E-06
55E-06
12E04
23E-05
1 4E-08
55E-06
55E06
51E-05
6 BE -06
61E-04
33E-04
55E-06
30E-08
1 3E-05
1 3E-05
19E-05
25E-04
55E06
55E-06
64E-05
2 5E-04
3 BE -04
55E-06
108E-11
678E-11
895E-11
166E-10
1 09E 10
1 24E 09
6 15E-09
877E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
N1 max
Nl max
Nt max
Nl max
Nl max
N1 max
Nl max
Nt max
Nl max
Nlmax
N1 max
Nt max
Nl max
Nt max
Nl max
Nt max
Nl max
Nl max
Nl max
N1 max
Nt max
Nl max
Nl max
Nt max
N1 max
Nl max
Nt max
Nl max
Nl max
Nt max
Nt max
Nlmax
Nl max
Nlmax
Nt max
Nl max
Nlmax
Nl max
Nl max
Nt max
Nl max
Nl max
Nl max
N1 max
Nt max
Nt max
Ht ma,
Nl max
Nl max
Nl max
Adult
Cancer
Risk
NT
NT
NT
NT
87E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 9E-12
15E-11
1 4E-12
NT
NT
NT
NT
NT
NT
95E-12
1 5E-12
NT
NT
74E-13
NT
98E-10
NT
NT
22E-11
68E-11
1 BE It
33E 11
22E-1I
25E-11
1 2E 11
t BE It
35E It
4 7E 10
29E-10
2 7E 10
30E-10
Child 1
Cancer
Risk
NT
NT
NT
NT
2 2E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 7E-12
3 7E-11
35E-12
NT
NT
NT
NT
NT
NT
24E-11
3.7E-12
NT
NT
1 8E-12
NT
24E-09
NT
NT
54E-11
1 7E-10
45E-11
BSE 11
54E 11
62E-11
3 IE-It
44E 11
86E 11
t 2E 09
7 IE 10
6 7E 10
75E 10
School-age
Cancer
Risk
NT
NT
NT
NT
1 3E 08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
29E-12
22E-11
21E-12
NT
NT
NT
NT
NT
NT
1 4E-11
22E-12
NT
NT
1 1E-12
NT
15E-09
NT
NT
33E-11
1 OE-10
27E-11
50E-11
33E 11
37E 11
1 9E 11
26E 11
52E II
70E 10
43E 10
40E 10
45E 10
Farmer
Cancer
Risk
NT
NT
NT
NT
1 9E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
42E-12
33E-11
31E-12
NT
NT
NT
NT
NT
NT
21E-11
3.3E-12
NT
NT
1 6E 12
NT
22E-09
NT
NT
48E-11
1 5E-10
40E-11
74E-11
49E 11
55E 11
2 7E 11
39E 11
7 7E It
10E 09
64E 10
60E 10
67E 10
                                                                                                                                         Adult      Child   School-age  Faimer

                                                                                                                                       Noncancer Noncancer Noncancer Noncancer

                                                                                                                                          HQ       HO       HO       HO
NT
40E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
47E-06
76E-08
NT
3 BE -09
76E-08
NT
33E-08
NT
76E-08
NT
2 IE-OS
94E-08
22E-06
1 6E-08
40E-08
NT
18E-08
13E-06
NT
51E-07
23E-08
NT
47E-07
NT
79E-08
1 1E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
IIT
NT
NT
15E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-05
29E-07
NT
14E-08
29E-07
NT
1 2E-07
NT
29E-07
NT
80E-08
3 5E-07
83E-06
60E-08
15E-07
NT
88E08
49E-06
NT
19E06
86E-08
NT
18E-06
NT
30E-07
43E09
NT
NT
NT
NT
NT
rir
m
NT
tn
NT
(IT
NT
NT
NT
90E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE-OS
1 7E-07
NT
86E-09
1 7E-07
NT
74E-08
NT
1 7E-07
NT
4 BE 08
21E07
50E 08
36E-08
90E-08
NT
41E-08
2.9E-06
NT
1 2E-06
S2E-08
NT
1 IE 06
NT
1 BE 07
26E-09
NT
NT
NT
NT
NT
NT
fU
NT
NT
NT
NT
NT
fJI
NT
40E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
47E-06
76E-08
NT
3 BE 09
76E-06
NT
3 3E-08
NT
76E-08
NT
2 IE 06
9 4E-06
22E06
1 6E-08
40E-08
NT
1 BE -08
13E-06
NT
5 1E-07
2 3E-06
NT
4 7E-07
NT
79E-08
1 IE 09
NT
NT
NT
NT
MT
NT
NT
NT
NT
NT
NT
NT
MT
Volume V. Appendix V-14
-------
T/BLE 16  Maximum Inhalation Risks and Moncancer HQs in Subaiea Ml
CHEMICAL
1 2,3.7,8,9 HxCDF
t. 2,3.4.6.7.8 HpCDF
1 2,3.4.7.8.9-HpCOF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Laid
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NO*)
Total sulfur oxides (SOx)
Paniculate matter
Resplrable participates
Inhalation
Slope
Factor
(mg/kg-d)* -1
1 5E«04
1 5E»03
1 5E«03
1 5E«02

NA
NA
50
NA
84
6 t
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E-05
36E05
1 3E-03
1 3E-04
13E-03
25E-01
NA
NA
2 1E 05
50E03
1 3E 03
1 3E 03
1 BE 05
7 5E-02
SOE^M
NA
NA
NA
NF
Emission
Rate
(B'sec)
293E-10
9 30E-09
1 22E-09
1 89E 08
4 2 BE 08
24E-04
' 42E-06
37E-05
15E04
33E-08
16E-05
7 1E-07
7tE^)7
94E-05
43E-05
1 4E 03
50E08
47E^4
1 5E 05
34E05
1 2E^>4
3 2E-02
24E*00
9 IE 02
72E^)2
7 2E 02
Subarea
N1 max
N1 max
N1 max
Nt max

N1 max
N1 max
Nt max
N1 max
N1 max
Nlmax
N1 max
Nlmax
Nt max
Nf max
Nlmax
N1 max
N1 max
N1 max
N1 max
Nt max
N1 max
N1 max
N1 max
N1 max
Nlmax
on s«e
Vapor
Cone
(ug/m3)
1 1E-10
35E 09
46E-10
72E09

9 IE-OS
1 6E-06
14E-05
57E-05
1 3E^)8
6 1E-06
27E-07
2 7E-07
36E-05
1 6E-O5
5 3E 04
1 9E-06
1 BE -04
57E 06
1 3E 05
46E-05
12E-02
92E-OI
35E-02
27E-02
2 7E 02
Cancer
Adult
Dose
(mg/kgd)
39E-15
1 2E-t3
1 6E-14
25E-13
57E-13
32E09
56E-11
50E-10
20E-09
44E 13
2 1E-10
95E-12
95E 12
1 3E-09
58E-10
1 9E-08
67E-11
63E-09
20E-10
45E-10
1 6E-09
4 3E-07
3 2E 05
1 2E 06
96E-07
96E-07
Cancer
Child
Dose
(mg/kgd)
98E-15
3 1E-13
4 1E-14
63E-13
1 4E-12
80E-09
1 4E 10
1 2E-09
50E-09
1 1E-12
53E-10
24E-11
24E-11
3 1E-09
1 4E-09
4 7E-08
1 7E-1Q
1 6E-08
50E-10
1 1E-09
40E-09
1 1E-06
61E-05
30E-06
24E 06
24E-06
Cancel
School-age
Dose
(mg/kgd)
59E-15
1 9E-13
2 5E-14
3BE-13
86E-13
48E-09
85E-11
75E-10
30E-09
66E-13
32E-10
1 4E-11
14E-11
19E-09
87E 10
2 BE 08
1 OE-10
95E-09
3 OE-10
68E-10
24E-09
6 4E-07
49E-05
1 8E-06
1 5E 06
1 5E-06
Cancer
Farmer
Dose
(mg/kg-d)
87E 15
28E-13
36E-14
56E 13
1 3E-12
7 1EX»
1 2E-10
1 1E-09
45E-09
98E-13
48E 10
2 1E-11
21E-11
28E-09
1 3E-09
4 2E-08
1 5E-10
1 4E-08
45E 10
10E-09
36E^)9
95E-07
7 2E-05
27E-06
2 1E-06
2 1E 06
Noncancer
Adult
Dose
(mg/kg d)
30E 14
97E-13
1 3E-13
20E-12
44E 12
2 5E-08
44E 10
39E 09
16E06
34E 12
1 7E 09
74E-11
74E 11
9 BE -09
45E09
1 5E-07
52E-10
4 9E 08
16E09
35E09
1 2E 08
33E-06
25E 04
95E06
75E06
75E-06
Noncancer
Child
Dose
(mg/kg-d)
1 IE 13
36E-12
4 7E-13
74E 12
1 7E-11
9 3E 08
16E-09
1 4E 08
58E-08
1 3E-11
62E-09
28E-10
2 BE- 10
37E-08
1 7E 08
5 4E-07
19E-09
1 BE 07
58E-09
1 3E-08
4 7E 08
12E05
9 4E 04
35E 05
2 BE 05
2 BE 05
Noncancei
School age
Dose
(mg/kg-d)
69E-14
22E 12
29E-13
45E-12
10E-11
56E08
99E-10
87E09
3 5E-08
78E-12
38E-09
1 7E-10
1 7E-10
2 2E-08
1 OE 08
3 3E 07
12E-09
1 IE 07
35E^)9
80E 09
28E-08
75E06
5 7E 04
2 IE 05
1 7E 05
1 7E 05
Noncancer
Farmer
Dose
(mg/Vg-d)
30E 14
97E 13
1 3E-13
20E 12
44E 12
2 5E 08
44E-10
3 9E 09
16E-08
34E 12
1 7E 09
74E-11
74E-11
9 BE 09
45E09
1 5E 07
52E 10
49E 08
1 6E 09
35E 09
1 2E-08
33E 06
2 5E 04
95E06
75E06
75E-06
-JOTES
  NA - Not applicable
  NF - Not found
  NT > No loxicity informatron
  HQ > Hazard quotient
  HI  'Hazard Index
 olume V, Appendix V-1 *
-------
TABLE 16  Maximum >....nation Risks and NoncancerHQs in Subaiea N1
CHEMICAL
1.2,3.7.8.9-HxCDF
1.2.3.«,6.7.8-HpCDF
1.2,3,4,7.8.9-HpCDF
OCDF
Dloxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NO)
Total sulfur oxides (SOx)
Paniculate mailer
Resplrable particulates
Inhalation
Slope
Factor
(mg/kg-d)"-1
1 5E*04
1 SE+03
1 5E*03
1 5E*02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0 004375
0000438
0004375
0875
NA
NA
0000075
00175
0 004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
IDE -04
75E-05
36E-OS
1 3E-03
13E-04
1 3E-03
25E-01
NA
NA
21E-05
50E-03
1 3E 03
1 3E-03
1 BE -05
75E^)2
50E-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E-09
189E-08
428E-08
, 24E-04
42E46
37E-05
15E-04
33E-08
16E-05
71E-07
71E-07
94E^>5
43E-05
1 4E-03
50E-08
47E-04
1 5E-05
34E-05
1 2E-04
32E-02
24E+00
91E^)2
72E-02
72E-02
Subarea
N1 max
N1 max
N1 max
N1 max

Nlmax
N1 max
N1 max
Nt max
N1 max
Nlmax
N1 max
Nlmax
N1 max
N1 max
N1 max
N1 max
Nt max
N1 max
N1 max
N1 max
Nlmax
N1 max
N1 max
N1 max
Nlmax
Adult
Cancer
Risk
59E-11
1 9E-10
25E 11
38E-11
1 9E-09
NT
NT
25E-08
NT
37E-12
13E-09
39E-10
NT
NT
NT
NT
5 6E-1 1
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
1 5E-10
47E-10
61E-11
95E-11
47E-09
NT
NT
62E-08
NT
92E-12
33E-09
9 7E-10
NT
NT
NT
NT
1 4E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
89E-11
28E-10
37E-11
57E-11
28E-09
NT
NT
3.7E-08
NT
56E-12
20E-09
5 9E-10
NT
NT
NT
NT
85E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
1 3E-10
41E-10
54E-11
85E-11
42E-09
NT
NT
5 5E-08
NT
82E-12
29E-09
87E-10
NT
NT
NT
NT
1 2E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                            Adult      Child   School-age   Farmer
                                                                                                                                          Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                             HQ       HQ       HQ       HQ
NT
NT
NT
NT
NT
NT
44E-08
51E-05
44E-04
27E-09
1 3E-05
5 9E-08
30E-10
NT
NT
6 BE -03
10E-07
39E-05
12E-08
20E-04
1 7E-07
67E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E-05
19E-04
1 6E-03
IDE 08
50E-05
2 2E-07
t 1E-09
NT
NT
2 5E-02
3 9E 07
15E04
47E-06
76E-04
6 2E-07
25E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
99E-08
1 2E-04
99E04
62E-09
30E-O5
1.3E-07
6 7E-10
NT
NT
1 5E-02
2 3E 07
8 BE -05
28E-06
46E-04
3 BE -07
1 5E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
44E06
5 IE-OS
4 4E-04
27E-09
13E05
5 9E 08
30E-10
NT
NT
6 BE -03
1 OE-07
39E-05
1 2E-06
2 OE 04
1 7E-07
6 7E-03
NT
NT
NT
NT
                                                                              Total Risk   4 2E-08    1 OE-07   6 3E-08   9 3E-08
                                                                                                                                  Total HI    16E-02   60E-02   36E02   1 BE 02
NOTES:
  NA" Not applicable
  NF-Not found      \
  NT « No toxlcity Information
  HQ - Hazard quotient
  HI -HazardIndex
Volume V, Appendix V-14
-------
 TABLE 1 7  Maximum Inhalahon Risks and Noncancei HOs in Sub.irra tl?
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrytonttrile
Anthracene
Benzene
Benzole acid
Benzotrichloride
Benzo(a)anthchloiobenzidme 3 3'-
"hchlorobiphenyl
Inhalation
Slope
Factor
(mg/kg d)*-1
NA
NF
7 7E-03
NA
NA
2 4E^1
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
t 1E»00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E^)2
1 3E«00
NF
NA
NA
2 7E-01
NA
8 1E^)2
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
MA
NA
NA
NA
NA
NA
NA
RAC
(rng/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
MA
00175
NA
02
005
NA
NA
Inhalation
RfD
(mg/kg d)
1 5E-02
NF
64E 04
25E 02
25E 02
1 4E 04
75E 02
43E 04
1 OE»00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E 03
50E 03
50E 03
36E-04
NA
7 IE 02
50E 02
7 IE 04
1 4E 04
1 5E 05
NF
1 OE 03
1 4E 03
50E 03
7 IE 01
2 5E-03
NA
20E 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
64E 04
NA
tIA
50E-03
NA
5 7E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E 06
6 7E 06
30E 04
29E 03
2 9E-04
2 OE-04
55E 06
1 5EO5
, 1 1E 05
32E 05
55E4)6
55E 06
55E 06
SSE^W
55E 06
6 7E 06
1 3E 05
6 7E 06
3 7E-05
1 OE 04
55E 06
49E 04
6 7E 06
5 1E 05
55E 06
89E 05
1 6E 04
55E 07
6 7E 06
67E 06
55E 06
3 7E 05
49E 04
2 7E 04
2 5E 04
67E 06
55E 06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
S5E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
N2max
N2 max
N2 max
N2 max
N2 max
N2 max
N2max
N2ma>
N2 max
N2 max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2 max
N2max
N2max
N2 max
N2max
N2 max
N2max
N2max
N2 max
N2max
N2 max
N2max
N2max
N2max
N2ma*
N2 max
N2max
N2 max
til max
N2 max
N2 max
N2 max
N2 ma»
N2ma«
N2 ma*
112 mai
N2 ma«
N2 ma*
N2 ma«
N2 man
N2 ma*
N2 ma<
Ofl site
Vapor
Cone
(ug/m3)
94E 07
94E 07
42E 05
4 IE 04
4 1E 05
2 BE 05
7 7E 07
2 1E-06
1 6E 06
45E 06
7 7E 07
7 7E 07
7 7E 07
7 7E 07
7 7E 07
94E 07
1 9E 06
94E 07
52E06
1 4E 05
7 7E 07
69E05
94E 07
7 2E 06
7 7E 07
1 2E 05
22E 05
7 7E 08
94E07
9 4E 07
7 7E 07
52E 06
69E 05
3 7E 05
3 4E 05
94E 07
7 7E 07
94E 07
7 7E-07
7 7E 07
7 7E 07
7 7E 07
1 9E 05
7 7E 07
7 7E 08
7 7E 07
3 7E 06
7 7E 07
7 7E 07
7 7E 07
4 7E 06
66E 09
Cancer
Adult
Dose
(mg/kg d)
33E 11
33E 11
1 5E 09
1 4E 08
1 4E 09
1 OE 09
2 7E 11
73E 11
56E 11
1 6E 10
27E 11
2 7E-11
2 7E 11
2 7E 11
27E-11
33E 11
66E 11
33E 11
1 8E 10
5 1E 10
2 7E-11
2 4E 09
33E 11
25E 10
2 7E 11
44E 10
7 BE 10
27E 12
33E 11
33E-11
2 7E 11
1 8E-10
2 4E 09
1 3E 09
1 2E 09
33E 11
2 7E 11
33E 11
2 7E It
2 7E 11
2 7E 11
2 7E II
69E 10
2 7E 11
2 7E 12
2 7E 11
1 3E 10
2 7F 11
2 71 11
? 7E 11
1 GE 10
? 3F 13
Cancer
Child
Dose
(mg/kg d)
82E-11
82E 11
3 7E 09
3 6E 08
36E 09
25E 09
68E 11
1 BE 10
1 4E 10
39E 10
6 BE 11
68E It
6 BE 11
68E 11
6 BE 11
82E 11
1 6E 10
82E 11
46E 10
1 3E 09
68E-11
60E-09
82E 11
63E 10
68E-11
1 1E 09
19E-09
6 BE- 12
82E 11
82E-11
68E 11
45E-10
60E 09
33E 09
30E09
82E 11
68E-11
82E 11
68E 11
68E 11
6 BE 11
6 BE 11
1 7E 09
6 8E 11
68F 12
68E 11
3 2E 10
68F 11
6 8[ 11
6 BE 1 1
4 IE 10
5 f)E 11
Cancer
School age
Dose
(mg/kg d)
50E 11
50E 11
22E 09
2 2E 08
22E 09
1 5E 09
4 IE 11
1 IE 10
84E 11
24E 10
4 1E-11
4 IE It
4 1E 11
4 IE 11
4 1E-11
50E-11
99E 11
50E 11
2 BE 10
77E 10
4 1E-11
36E^)9
50E-11
3 BE 10
4 IE 11
86E 10
1 2E-09
4 1E-12
50E-11
50E-11
4 IE 11
27E-10
36E09
20E^)9
1 BE 09
50E 11
4 IE tl
50E 11
4 IE 11
4 1E-11
4 1E-11
4 1E 11
1 OE 09
4 IE 11
4 IE 12
4 IE 11
20E 10
4 IE 11
4 1C 11
4 IF It
2 5E 10
3 V 11
Cancer
Faimei
Dose
(mg/kg d)
73E 11
73E 11
33E 09
32E 08
32E 09
22E 09
60E 11
16E 10
1 2E 10
35E 10
60E 11
60E 11
60E 11
60E 11
60E-11
73E 11
1 5E-10
73E-11
41E 10
1 IE 09
60E 11
5 4E 09
73E 11
56E 10
60E 11
9 BE 10
1 7E 09
60E 12
73E 11
73E 11
60E 11
40E 10
54E09
29E09
2 7E 09
73E-11
60E 11
73E-11
60E 11
60E 11
60E-11
60E-11
1 5E 09
60E 11
60E 12
6 OF 11
2 9E 10
6 OE 11
6 OF 11
6 OE 11
3 nf 10.
r> 1 f 11
Noncancer
Adult
Dose
(mg/kg-d)
26E 10
26E-10
1 2E 08
1 IE 07
1 IE 08
7 7E 09
2 1E 10
56E 10
43E-10
1 2E-09
2 1E 10
2 IE 10
2 1E-10
2 IE 10
2 IE 10
26E 10
5 1E-10
26E 10
1 4E 09
40E 09
2 IE 10
1 9E 08
26E-10
20E 09
2 1E 10
34E 09
6 IE 09
2 IE 11
26E 10
26E 10
2 1E 10
1 4E 09
1 9E 08
1 OE 08
94E*9
26E-10
2 IE 10
26E 10
2 1E 10
2 1E 10
2 1E 10
2 IE 10
5 3E 09
2 IE 10
2 IE 11
2 IE 10
1 OE 09
2 IF 10
2 IF 10
2 IF 10
1 3f 09
1 Hf 12
Noncancei
Child
Dose
(mg/kg-d)
96E 10
96E 10
4 3E 08
42E 07
4 2E-08
2 9E 08
79E-10
1 IE 09
1 6E-09
4 6E-09
79E-10
79E-10
79E-10
79E-10
79E-10
96E-10
1 9E-09
96E-10
53E D9
1 5E-08
79E 10
7 OE 08
96E 10
74E09
79E 10
1 3E-08
2 3E 08
79E 11
96E-10
96E 10
79E 10
5 3E 09
70E 08
3 BE 08
35E 08
96E 10
79E-10
96E 10
79E 10
79E-10
79E 10
79E 10
2 OE 08
79E 10
79E 11
7 9E 10
38F 09
7 
-------
TABLE 17  Maximum Inhalation Risks and Noncancer HQs in Subarea N2
CHEMICAL
Acenapnthane
Acenaphthylene
AeetaWehxde
Acetone
Acetophenone
AcrytonHrlla
Anthracene
Benzene
Benzole acid
Benzotrfchlofide
B*nzo(a)anthracen«
Benzo(a)pyrene
Benzo(b)l)uoranlhene
Benzo(g,h ,i)pecylena
Banzo(k)nuoranthane
Bis(2-chloroethoxy) methane
Bis(2-chk>ioelhyl)elher
Bls(2-chk>rolsopropyl)«th«r
Bls(2-ethylhexyl)phthalaie
Bromodlchlofomethane
Bromoform
Bromomethane
Btomodlphenyl ether, p-
Butanone. 2- (Methyl ethyl ketone)
Butyl be rurylphthalat*
Carbon disulfkle
Carbon tetrachloride
Chlordane
Chloro-3-methylphenol. 4-
Chloroaniline. p- (4-Chloroanillne)
Chloiobenzane
Chtorobenzilata
Chloroethane (Ethyl chloride)
Chloroform
Chloroirmthane
Chloronaphlhalane. beta
Chlorophenol, 2- •
Chlorodiphenyl ether. 4-
Chrysene
Cresol. m-
Cresol. o- (2-Methylphenol)
Cresol. p-
Crotonaldehyde
Cumena
DDE. 4,4'-
Dibenz(a ,h)anthracene
Dibromochloromethana
Dichlorobenzene. 1 .3-
Dichlorobenzene. 1 .4-
Dichloroberuene. 1 ,2-
Dichlorobenzidine. 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)A-t
NA
NF
7 7E-03
NA
NA
2 4E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
27E-01
NA
8 1E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA •
NA
NA
NA
NA
RAC
(mgmi3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
0.0005
0000053
NF
00035
0005
00175
25
000875
NA
007
0 004375
NF
NA
0 0437S
0 04375
0 004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mo/kg-d)
15E-02
NF
6 4E-04
2 5E-02
2 5E-02
1 4E-04
7 5E-02
43E-04
IDE +00
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E-03
50E-03
5 OE-03
36E-04
NA
7 1E^)2
50E-02
7 1E-04
1 4E-04
15E-05
NF
1 OE-03
1 4E-03
5 OE-03
7 IE 01
2 5E-03
NA
2 OE 02
1 3E-03
NF
NA
1 3E-02
1 3E-02
1 3E-03
NA
64E 04
NA
NA
50E 03
NA
57E 02
1 IE 02
NA
NA
Emission
Rate
(g/sec)
67E-06
67E 06
30E-04
2 9E-03
29E04
20E-04
55E06
15EX»
1 IE 05
32E05
55E-06
55E06
55E-06
55E-06
55E-06
67E-08
13E^»
67E-08
37E-05
10E^>4
55E-06
49E04
67E-06
5 IE-OS
55E-06
89E-05
1 6E-04
5 5E-07
B7E-06
67E-06
55E-06
37E05
4 9E-04
2 7E-04
2 5E 04
67E 06
55E 06
67E 06
55E 06
55E 06
55E 06
55E06
1 4E 04
55E 06
55E 07
55E 06
26E OS
55E 06
55E 06
5SE 06
33E 05
4 7E 08
Subatea
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2max
N2 max
N2 max
N2max
N2 max
N2max
N2 max
N2max
N2max
N2 max
N2 max
N2 max
N2 max
N2max
N2max
N2 max
N2 max
N2 max
N2 max
N2max
N2max
N2 max
N2max
N2 max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2max
N2 max
N2ma«
N2ma
N2ma
N2 ma
N2ma
112 ma
142 ma
N2 ma
N2 ma
fJ2ma
r<2 ma
f/2ma
AduH
Cancer
Risk
NT
NT
1 1E-1t
NT
NT
24E-10
NT
21E-12
NT
NT
NT
NT
NT
NT
NT
NT
72E-11
NT
NT
NT
10E-13
NT
NT
NT
NT
NT
41E-11
35E-12
NT
NT
NT
50E-11
NT
1 1E-10
76E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
(U
til
m
tIT
(IT
NT
NT
Child
Cancer
Risk
NT
NT
28E-11
NT
NT
59E-10
NT
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
NT
NT
NT
26E-13
NT
NT
NT
NT
NT
10E-10
8 7E-12
NT
NT
NT
1 2E-10
NT
26E-10
19E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
nr
(JT
III
m
nr
nr
in
nr
School-age
Cancer
Risk
NT
NT
1 7E 11
NT
NT
36E-10
NT
32E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
1 6E-13
NT
NT
NT
NT
NT
62E11
53E-12
NT
NT
NT
75E-11
NT
1 6E-10
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
nr
in
nr
tir
fir
Farmer
Cancer
Risk
NT
NT
25E-11
NT
NT
53E-10
NT
47E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
23E-13
NT
NT
NT
NT
NT
9 IE 11
78E-12
NT
NT
NT
1 1E-10
NT
23E-10
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HT
nr
fir
NT
nr
(I!
fir
                                                                                                                                           Adult      Child   School-age  Farmer
                                                                                                                                         Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HQ       HQ       HQ
1 7E-08
NT
1 BE -05
44EO6
4 5E-07
54E-05
28E-09
13E06
4 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
26E-08
29E-07
79E-07
42E-00
53E-05
NT
28E-08
42E-09
48E-06
4 2E-05
1 4E-06
NT
26E-07
15E47
2 BE -07
26E-OS
4 IE-OS
NT
13E4»
1 7E-07
NT
NT
17E4W
1 7E-08
1 7E-07
NT
3 3E-07
NT
nr
20E 07
NT
37E 09
1 5E 08
m
W
6 4E-08
NT
6 7E-05
1 7E-05
1 7E-06
20E-04
1 1E-08
49E-06
16E09
NT
NT
NT
NT
NT
NT
NT
NT
96E-08
1 1E-06
30E-06
1 6E 07
20E-04
NT
1 OE 07
1 6E-08
18E05
1 6E-04
53E-06
NT
9 6E-07
55E07
1 1E-06
9 BE -08
1 5E-05
NT
4 BE -08
6 3E-07
NT
NT
63E 08
63E08
63E 07
NT
1 2E 06
NT
m
75F 07
nr
1 4E 08
55F 08
nr
nr
39E-08
NT
4 IE-OS
1 OE 05
IDE -06
1 2E 04
63E-09
30E-06
98E-10
NT
NT
NT
NT
NT
NT
NT
NT
5 BE -08
64E-07
18E-06
95E08
1 2E-04
NT
6 2E-08
95E09
1 1E-05
96E05
32E-OB
NT
5 BE -07
3 3E 07
6 4E-07
59E08
92E-06
NT
29E 08
3 BE -07
NT
NT
3 BE 08
3 BE 08
3 BE 07
NT
7 IE 07
NT
HT
4BF. 07
NT
83E 09
3 IE 08
IIT
nr
1 7E-08
NT
18E05
44E-06
4 5E-07
54E05
28E-09
13E-06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
26E-08
2 9E-07
7 9E 07
42E-08
53E-05
NT
2 BE -08
42E09
4 BE 08
42E-05
1 4E-OB
NT
2 6E-07
1 5E 07
2 BE 07
26E08
4 IE 06
NT
1 3E-OB
1 7E-07
NT
NT
1 7E 08
1 7E 08
1 7E 07
NT
33E 07
NT
NT
20E07
NT
37E 09
1 5E 08
tir
NT
Volume V. Appendix V-14
-------
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-------
TABLE 17  Maximum It,, _.ation Risks and Noncancef HQs in Subaiea N2



CHEMICAL
Dichlorodffluoromethane
Dichloroethane, 1,1- (Ethylidene dichloride)
Dichloroethane. 1 ,2-
Oichloroethcn*. 1,1- (Vmylldine chloride)
Dlchlotoethene (trans), 1 ,2
Dlchlotophenol. 2,4-
Dichlofopropane, 1.2- (Propytone dlchlotide)
Dichloropropene (cis). 1.3-
DtehloroprofMn* (trans), 1 .3-
DiatnylpnthMala
Dtmelhoxyboftttdme, 3,3'-
Dimrthytphenol, 2.4-
DlnMttiytpnttwIate
Oi-n-buty)phthalate
Dintfrototuene. 2.6-
Dinitro-2-methylphenol. 4,6-
DlnHropnanol, 2.4-
DinttroMuene. 2.4-
Dioxine, 1.4-
Dl(n)octy1 phthalate
D, 2.4-
Ethyl m»tn«cn/)ate
Ethylbenisrve
Ethyt«ne dibfomide
Ethylena oxide
EthyUne thlourea
Fruorinthene
FhMMene
Formaldehyde
Furfural
HftptBCnlof
Heptachtofoblphenyf
Hexachlorobenzenu
Hexachloroblphenyl
Hexachlorobirtadlene
Hexachlorocyclohexane, gamma (Llndane)
Hexachlorocyclopentadiene
Hexachloro«tharve \
Hexachlorophene
Hexanone, 2-
lnd«no(1 ,2.3-cd)pyrene
Isophorone
Maleic hydrukto
Mettioxychlor
Methyf-t-butyl ether
Methyi-2-Pentanone, 4- (MIBK)
Methylen* chloride
Methylnaphthalene. 2-
Monochlorobiphenyl
Naphthalene
Nitroaniline. 2-
Nitroanihne, 3-
Inhalation
Slope
Factor
(mg/kg-d)*-1
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
1 3E-01
13E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
3 5E-01
NA
NA
NA
4SE-02
NA
45E+00
NA
1 6E+00
NA
7 BE -02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA
NA
NF


RAC
(mg/m3)
005
012S
NA
0007875
00175
0 002625
0001
0005
0005
0.7
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
0 07875
025
000005
NA
000007
0035
0035
0.175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0004375
075
002
0 75
NF
NA
0035
000005
NF

Inhalation
R»D
(mfl/kfl-d)
1 4E-02
36E-02
NA
2 3E-03
5 OE-03
75E-04
2 9E-04
1 4E-03
14E-O3
20E-01
NA
5 OE-03
NA
25E42
25E-04
NF
50E-04
50E-04
NA
5 OE-03
2 5E 03
23E-02
7 1E-02
14E-05
NA
20E05
10E-02
IDE -02
50E02
36E-03
1 3E-04
NA
20E-04
NA
50E-05
75E-05
50E-06
2 5E-04
75E-05
NF
NA
50E-02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 1E-01
NF
NA
1 OE 02
1 4E-05
NF

Emission
Rate
(g/sec)
25E04
3E-05
3E-05
3E-05
3E-05
5E-06
3E-05
3E-05
. 3E-05
7E-05
2E-04
55E-06
55E-06
16E-05
55E-06
55E^»
55E-06
55E-06
49E-04
556-06
39E05
25E-04
50E-04
1 2E-04
31E-05
1 5E 10
55E-08
87E-06
61E-04
55E-06
55E-07
1 4E-08
55E-06
1 4E 08
1 OE 04
55E-05
55E06
55E-06
32E-05
64E-05
55E-06
67E-06
1 2E 04
55E07
1 3E-05
1 3E 05
4 OE-04
4 2E 05
1 7E 08
55E 06
67E 06
6 7E-06



Subarea
N2max
N2 max
N2max
N2max
N2max
N2max
N2 max
N2 max
N2max
N2 max
N2max
N2max
N2max
N2max
N2max
N2max
N2 max
N2 max
N2max
N2max
N2max
N2max
N2 max
N2 max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2max
NJmax
N2 max
N2max
N2 max
N2max
N2max
N2max
N2 max
N2 max
N2 max
N2 max
N2 max
N2max
N2 max
til max

Adult
Cancer
Risk
NT
NT
56E-12
74E-11
NT
NT
NT
80E-12
80E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
43E-10
53E-11
NT
NT
NT
1 3E-10
NT
1 2E-1 1
NT
4 4E-1 1
NT
39E-11
NT
NT
38E-13
NT
NT
NT
NT
NT
NT
NT
NT
32E 12
NT
NT
NT
NT
NT

Child
Cancer
Risk
NT
NT
1 4E-11
1 8E-10
NT
NT
NT
20E-11
20E-I1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 09
1 3E-10
NT
NT
NT
34E-10
NT
30E-11
NT
1 1E-10
NT
97E-11
NT
NT
95E-13
NT
NT
NT
NT
NT
NT
NT
NT
80E-12
NT
NT
NT
NT
NT

School-age
Cancer
Risk
NT
NT
84E-12
1 1E-10
NT
NT
NT
12E-11
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 5E-10
79E-11
NT
NT
NT
20E-10
NT
1 BE-11
NT
66E-11
NT
5 BE-11
NT
NT
57E-13
NT
NT
NT
NT
NT
NT
NT
NT
48E 12
NT
NT
NT
(IT
NT

Farmer
Cancer
Risk
NT
NT
1 2E-11
16E-10
NT
NT
NT
1 BE-11
18E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
96E-10
1.2E-10
NT
NT
NT
30E-10
NT
27E-11
NT
97E-11
NT
B6E-11
NT
NT
84E-13
NT
NT
NT
NT
NT
NT
NT
NT
7 IE 12
NT
NT
NT
NT
NT
                                                                                                                                           Adult      Child   School-age  Farmer
                                                                                                                                         Noncancer Noncancer Noncancef Noncancer
                                                                                                                                            HQ       HO       HQ       HQ
6 6E-07
1 3E-08
NT
2 1E-07
9 6E-08
2 BE -07
1 7E-06
3 4E-07
3 4E-07
32E-09
NT
42E-08
NT
24E-08
B.4E-07
NT
4 2E-07
42E-07
NT
42E-08
60E-07
42E-07
27E47
31E-04
NT
2 BE-10
21E-00
26E-08
4,7E-Or
59E-08
17E-07
NT
1 1E-06
NT
77E05
2 BE -05
42E05
8 4E-07
16E-05
NT
NT
5 IE 09
3 5E-08
1 7E48
2 2E 09
84E 08
7 IE 08
NT
NT
2 IE 08
1 8E 05
tJT
25E-06
50E-08
NT
8 OE-07
3 6E-07
1 1E-06
63E-06
13E-06
13E-06
12E-08
NT
1 6E-07
NT
90E-08
3.2E-06
NT
16E-06
1.6E-06
NT
1 6E-07
22EO6
16E-OB
10E-06
12E-03
NT
IDE -09
79E08
96E-08
17E-06
2 2E-07
63E07
NT
39E-06
NT
29E04
1 OE-04
16E-04
32E-06
61E05
NT
NT
19E 08
1 3E 07
63E 08
84E 09
3 IE 07
26E 07
NT
NT
79E 08
67E 05
NT
15E-06
30E-08
NT
4 8E-07
2 2E 07
6 3E-07
38E-06
7 6E-07
7 6E-07
73E-09
NT
95E-08
NT
54E-08
19E-06
NT
95E07
95E-07
NT
9 SE-08
1 3E-06
9 4E-07
60E-07
7 OE-04
NT
63E-10
4 BE -08
5 BE -08
1 1E 06
1 3E 07
3 BE -07
NT
24E-06
NT
17E04
6 3E-05
95E05
19E-06
37E-05
NT
NT
1 2E 08
80E 08
3 BE 08
5 IE 09
1 9E 07
1 6E 07
NT
NT
48E 08
4 1E 05
NT
6 6E-07
1 3E-08
NT
2 IE 07
9 6E-08
2 BE -07
1 7E-06
3 4E-07
3 4E 07
32E-09
NT
42E-08
NT
2 4E-08
84E-07
NT
42E07
42E-07
NT
4 2E-08
6 OE-07
4 2E 07
2 7E-07
3 1E-04
NT
2 BE 10
2 1E-08
2 6E OS
4 7E 07
59E-08
1 7E-07
NT
1 1E-06
NT
7 7E 05
2 BE 05
42E-05
84E-07
16E-05
NT
NT
5 IE 09
35E08
1 7E 08
22E 09
84EOB
7 IE 08
NT
NT
2 IE 08
1 8E 05
NT
Volume V, Appendix V-14
-------
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-------
TABLE 17  Maximum v   >tion Risks and Noncancet MQs in Subaiea N2
CHEMICAL
Nftroanlline. 4-
Nitrobenzene
Nit/ophancH. 2-
Nitrophenol, 4-
N Nltroso-dl-n-butylamlne
N Nitroso-dl-n-propylamlne
N-NHrosodlphenylamlne (Diphenylamlne)
Nonachloroblphenyl
Octachlorobipnenyl
Pentachtofobenzene
PantachloroWphenyl
Pent»chloronltrob»nzene
Pantachtorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Prop«nyl)-1 ,3-benzodloxole)
Styrene
Tetrachtorobtphenyl
Telrachloroelhane. 1.1.1.2-
Tatrachkxoethana. 1,1.2,2-
T etreehlof oethene
T atrachtofoph.no). 2.3.4.6-
Toluene
Trichloro-1.2.2-trMluoroelhane. 1.1.2-
Trichtofobenzene, 1.74-
Trichloroblphenyl
Trtchloroelhane. 1.1.1- (Methyl chloroform)
Trichloroethane, 1,1.2-
Trtchloroethene
Trtchtorofluofomethane
Trtehlorophenol. 2,4,5-
Trtcnlorophenol, 2,4,6-
Vlnyl acetate
Vinyl chloride
Xytine. m/p- (m/p-Dbnettiyl benzene)
Xylene, o- (o-Dimethyl benzene)
2.3.7,8-TCDO
1. 2.3,7.8 PCDO
1.2.3.4.7,8-HxCDO
1. 2.3.6.7.8 HxCDO
1.2.3.7.8,9-HxCDD
1.2.3.4.6.7,B-HpCDD
CCDD
2.3.7.8-TCDF
1. 2.3.7.8 PCDF
2.3,4.7.8-PCDF
1,2.3.4.7.8-HxCOF
1.2]3.67!8-HxCDF
2]3]4.6.7.8-HxCDF
Inhalation
Slope
Factor
(mg/kg-d)A-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
10E4I2
NA
30E-01
NA
NA
15E*05
7 5E+04
1 5E*04
1 5E»04
1 SE+04
1 5E»03
1 5E»02
1 5E+04
7 5E»03
7 5E+04
1 5E+04
1 5E+04
1 5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0175
00675
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
75E-03
NF
7 1E-02
NA
75E-03
NA
25E-03
75E-03
29E-02
2 1E+00
1 4E-02
NA
71E-02
1 OE-03
NA
50E-02
25E-02
NA
1 4E-02
NA
50E-01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E-06
55E-06
1 2E-04
67E-06
67E-06
1 4E-08
1 4E-08
4 BE -05
14E-08
34E^»
55E-06
67E-06
55E-06
55E-06
1 2E-04
23E-05
1 4E-08
55E-06
5SE-08
51E-05
68E-06
61E-04
33E-04
55E-06
30E-08
1 3E-05
1 3E-05
1 9E-05
2 5E 04
55E-06
55E-06
64E-05
256-04
3 BE -04
55E-06
1 08E-11
676E-11
B95E-11
1 66E-10
1 09E 10
1 24E 09
6 15E 09
877E-11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E-09
Subaraa
N2 max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2max
N2 max
N2max
N2 max
N2 max
N2 max
N2max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2max
N2 max
N2max
N2max
N2 max
N2 max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2 max
N2 max
H2 max
N2ma»
N2 max
N2 man
N2 max
N2 max
N2max
N2ma>
Adult
Cancer
Risk
NT
NT
NT
NT
32E^>9
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E-13
55E-12
51E-13
NT
NT
NT
NT
NT
NT
35E-12
55E-13
NT
NT
27E-13
NT
36E-10
NT
NT
80E-12
25E 11
66E-12
1 2E 11
8 1E 12
92E 12
45E 12
65E 12
1 3E 11
1 7E 10
1 IE 10
99E 11
1 1E-10
Child !
Cancer
Risk
NT
NT
NT
NT
8 OE-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-12
14E-11
13E-12
NT
NT
NT
NT
NT
NT
8 7E-12
1 4E-12
NT
NT
68E-13
NT
90E-10
NT
NT
20E-11
62E 11
16E 11
3 IE 11
20E 11
23E 11
1 IE 11
1 6E 11
32E 11
43E 10
26E 10
25E 10
28E-10
School-age
Cancer
Risk
NT
NT
NT
NT
48E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-12
B3E12
77E-13
NT
NT
NT
NT
NT
NT
53E-12
82E-13
NT
NT
41E-13
NT
55E-10
NT
NT
1 2E 11
38E-11
10E 11
1 8E-11
1 2E 11
1 4E 11
6 BE 12
9 BE 12
1 9E 11
26E 10
1 6E 10
1 5E 10
1 7E-10
Farmer
Cancer
Risk
NT
NT
NT
NT
72E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-12
1 2E-11
1.1E-12
NT
NT
NT
NT
NT
NT
78E-12
1 2E-12
NT
NT
60E-13
NT
81E-10
NT
NT
1 8E-11
56E-11
15E-11
27E-11
1 BE 11
20E 11
1 OE 11
1 4E It
2 BE 11
3BE-10
23E 10
2 2E 10
25E 10
                                                                                                                                          Adult      Child   School-age  Farmer
                                                                                                                                        Nbncancer  Noncancer Noncancar Noncancar
                                                                                                                                           HQ       HQ       HQ       HQ
NT
15E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
17E-06
2 BE -08
NT
14E-09
2 BE -08
NT
12E-08
NT
2 BE -08
NT
79E-07
35E-08
8 2E-07
59E-09
15E-O8
NT
87E-09
4 BE -07
NT
19E-07
84E-09
NT
1 7E-07
NT
29E48
4 2E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
tJT
NT
55E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E-06
1 1E-07
NT
53E-09
1 1E-07
NT
45E-08
NT
1 1E-07
NT
2.9E-06
1 3E-07
3 IE 08
22E-08
55E-OB
NT
2 5E-08
1.8E-06
NT
70E-07
32E08
NT
6 4E 07
NT
1 1E-07
16E-09
NT
NT
NT
NT
NT
W
tit
(IT
nr
in
NT
NT
nr
NT
33E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E-06
63E-08
NT
32E-09
63E-08
NT
27E-08
NT
63E-08
NT
18E-06
78E-08
19E-06
1 3E-08
33E-O8
NT
15E-08
1 IE-OS
NT
4 2E 07
1 9E-06
NT
39E^)7
NT
66E08
95E 10
NT
NT
NT
NT
NT
NT
NT
tIT
NT
NT
NT
NT
NT
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-06
28E-08
NT
1 4E-09
2 BE -08
NT
1 2E-08
NT
28E-08
NT
7 9E-07
35E08
8 2E 07
59E-09
1 5E-08
NT
67E-09
4 BE -07
NT
1 9E-07
84E-09
NT
1 7E 07
NT
2 9E 08
42E-10
NT
NT
NT
NT
NT
NT
NT
NT
HT
NT
NT
NT
tIT
 Volume V, Appendix V-14
-------
TABLE I 7  Maximum Inhalntion Risks and f Joncancer HQs in Sub.iroa N?
CHEMICAL
1 2,3.7.8.9 HxCDF
123467 B-HpCDF
1.2.3,4,7,8.9-HpCDF
OCOF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavatent)
Chromium (bivalent)
Copper
Lead
M ircury (ant) MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxidas (SOx)
Particulate matter
Resplrable particulars
Inhalation
Slope
Factor
(mg/kg-d)*- 1
1 5E+04
1 5E»03
1 5E*03
1 SE»02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAG
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0 004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/Vg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E^)5
1 3E-03
1 3E-04
1 3E-03
2 5E-01
NA
NA
2 IE 05
50E 03
1 3E-03
1 3E 03
1 8E 05
7 5E 02
50E 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E 09
1 89E 08
4 28E-08
2 4E 04
4 2E-06
37E-05
1 5E-04
33E08
16E-05
71EW
7 IE 07
94E«
43E^J5
1 4E 03
50E-06
47E-04
1 5E 05
34E 05
1 2E 04
32E-02
24E»00
91E4>2
7 2E 02
7 2E 02
Subafei
N2max
N2 max
N2max
N2 max

N2max
N2max
N2 max
N2max
N2 max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2 max
N2max
N2max
N2max
N2max
N2max
N2max
N2 max
N2max
Ofl site
Vapor
Cone
(ug/m3)
4 IE 11
1 3E 09
1 7E 10
2 7E-09

34E 05
5 9E-07
52E06
2 IE 05
46E-09
22E06
99E-08
99E 08
1 3E-05
60E-06
20E 04
7 OE-07
66E-05
2 1E-06
48E-06
1 7E-05
4 5E-03
34E 01
1 3E 02
1 OE 02
1 OE-02
Cancer
Adult
Dose
(mg/kg d)
1 4E 15
4 BE 14
60E 15
93E 14
2 1E-13
1 2E 09
2 IE 11
1 8E-10
74E 10
1 6E 13
79E-11
35E-12
35E-12
46E-10
2 1E-10
69E-09
25E-11
23E-09
74E 11
1 7E 10
59E-10
1 6E 07
1 2E05
45E07
3 5E 07
35E-07
Cancer
Child
Dose
(mg/kg d)
36E 15
1 1E 13
1 5E 14
23E 13
53E 13
2 9E 09
52E 11
45E-10
1 BE 09
41E-13
20E-10
87E 12
87E-12
1 2E-09
53E-10
1 7E 08
61E 11
5 BE 09
1 BE 10
42E 10
1 5E-09
39E-07
30E05
1 1E 06
88E-07
88E-07
Cancer
School age
Dose
(mg/kg-d)
22E 15
6 9E 14
9 1E 15
1 4E 13
32E-13
1 BE -09
3 IE 11
27E 10
1 1E-09
24E-13
1 2E-10
53E-12
53E 12
70E-10
32E-10
1 OE 08
37E 11
35E-09
1 1E-10
25E-10
89E-10
2 4E-07
1 BE -05
68E07
5 3E-07
5 3E 07
Cancel
Faimei
Dose
(mg/kg d)
32E 15
1 OE-13
1 3E 14
2 IE 13
4 7E-13
26E-09
46E-11
4 IE 10
16E09
36E-13
1 8E-10
78E-12
78E-12
10E-09
4 7E-10
1 5E 08
55E-11
5 IE 09
1 6E 10
37E 10
1 3E 09
35E07
2 7E 05
10E06
79E 07
7 9E 07
Noncancer
Adult
Dose
(mg/kg d)
1 IE 14
3 6E-13
47E 14
73E 13
1 6E 12
92E 09
1 6E-10
1 4E 09
5 BE 09
1 3E-12
61E-10
27E 11
27E 11
36E-09
16E09
54E08
1 9E-10
1 BE -08
58E 10
1 3E-09
46E 09
12E-06
93E05
3SE06
28E06
28E06
Noncancer
Child
Dose
(mg/kg-d)
42E 14
1 3E-12
1 7E-13
27E-12
61E-12
3 4E-06
60E-10
53E-09
2 IE 08
47E 12
23E-09
1 OE 10
1 OE-10
1 3E 08
62E-09
2 OE-07
72E-10
6 7E 08
2 1E 09
4 9E 09
1 7E 08
46E06
3 5E 04
1 3E-05
1 OE 05
10E-05
Noncancet
School-age
Dose
(mg/kg d)
25E-14
8 IE 13
1 IE 13
1 6E 12
37E 12
2 IE 08
36E 10
32E09
1 3E 08
29E 12
1 4E 09
61E-11
6 1E-11
8 IE 09
37E09
1 2E 07
43E-10
41E08
1 3E 09
29E 09
1 OE 08
2 BE 06
2 IE 04
79E-06
62E 06
62E-06
Noncancei
Farmer
Dose
(mg/kg-d)
1 IE 14
36E-13
47E 14
73E-13
16E-12
92E 09
1 6E-10
1 4E 09
5 BE 09
1 3E-12
6 IE 10
2 7E-11
2 7E-11
36E 09
1 6E 09
54E 08
1 9E 10
1 BE 08
5 BE 10
1 3E 09
46E 09
1 2E 06
93E 05
35E 08
2 BE 06
2 BE 06
MOTES.
  NA • Not applicable
  NF « Nol found
  NT - No toxicNy information
  HQ • Hazard quotient
  HI -Hazardindex
'olume V Appendix V-1 *•
-------
TABLE 17  Maximum v
                       ,ion Risks and Noncancet HQs in Subarea N2
CHEMICAL
1.2,3,7.8,9-HxCDF
1,2.3.4.6,7.8-HpCDF
1,2,3,4,7,8,9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavatont)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Resplrable parttculates
Inhalation
Slope
Factor
(mg/kg-d)*-1
1 5E+04
1 5E»03
1 5E»03
1 5E»02

NA
NA
SO
NA
64
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RtD
(mg/kg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E-05
1 3E-03
1 3E-04
13E-03
2 5E-01
NA
NA
2 IE-OS
50E-03
13E03
1 3E43
18E05
75E^J2
506-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E-09
1 22E-09
1 89E-08
428E-08
24E-04
42E-06
37E05
15E-04
33E-08
18E-05
71E-07
7 1E-07
94E05
43E-05
1 4E-03
50E-06
47E-04
15E4J5
34E-05
t 2E-04
32E-02
24E+00
91E-02
7 2E-02
7 2E-02
Subarea
N2max
N2 max
N2max
N2 max

N2max
N2max
N2max
N2 max
N2 max
N2max
N2max
N2max
N2 max
N2max
N2max
N2max
N2max
N2max
N2max
N2max
N2 max
N2max
N2max
N2m«x
N2max
Adult
Cancer
Risk
22E-11
69E-11
90E-12
1 4E-11
69E-10
NT
NT
S.1E-09
NT
1 4E-12
48E-10
1 4E-10
NT
NT
NT
NT
2 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
54E-11
1 7E-10
22E-11
35E-11
1 7E-09
NT
NT
23E-08
NT
34E-12
12E-09
36E-10
NT
NT
NT
NT
52E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
33E-11
1 OE-10
1 4E-11
21E-11
1 OE-09
NT
NT
1 4E-08
NT
2 IE 12
72E-10
2 2E-10
NT
NT
NT
NT
31E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
48E-11
1 5E-10
20E 11
31E-11
1 5E-09
NT
NT
20E-06
NT
30E-12
1 1E-09
32E-10
NT
NT
NT
NT
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                           Adult      Child    School-age  Farmer
                                                                                                                                         Noncancer Noncancer  Noncancer Noncancer
                                                                                                                                            HQ       HQ        HQ        HQ
NT
NT
NT
NT
NT
NT
16E-06
1 9E-O5
1 6E-04
1 OE-09
49E-06
2 2E-08
1.1E-10
NT
NT
2 5E-03
38E-06
14E-05
46E-07
74E-05
6 IE-OS
25E4I3
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E-06
7 IE-OS
6 OE 04
36E-09
1 BE -OS
B 1E-08
41E-10
NT
NT
9 4E-03
1 4E 07
54E-05
1 7E-06
2 BE -04
2.3E-O7
92E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E-06
43E-OS
36E04
23E439
1 IE-OS
4 9E-08
2 5E-10
NT
NT
5 7E-03
6 7E 08
33E-OS
10E06
17E-04
1 4E-07
S 5E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT.
16E06
19E05
1.6E-04
IDE 09
49E-06
22E-08
1.1E-10
NT
NT
25E-03
3 BE 08
1 4E-05
46E47
74E05
61E-08
25E-03
NT
NT
NT
NT
                                                                              Total Risk   1 5E-08   3 BE-OB   2 3E-OB   3 4E-O8
                                                                                                                                 Total HI   59E-03   22E-02   1 3E-02   59E-03
NOTES:
  NA » Not applicable
  NF • Not found
  NT - No toxldty information
  HO " Hazard quotient
  HI -HazardIndex
Volume V. Appendix V-14
-------
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-------
TABLE 18  Maximum,,    j'tion Risks and Noncancet HQs in Subarea N3
CHEMICAL
Acenaphthene
Acenaphthyiene
Acetaldahyde
Acetone
Acetophenone
Aciylontbile
Anthracene
Benzene
Benzole acid
Benzotrtchtortde
Benzo(a)anthracene
Benzo(a)pyrene
Bmzo(b)fluoranttiana
Benzo(g,h.l)perylene
Benzo(k)fluoranthane
Bts(2-chk>roethoxy) methane
Bls(2-chk»o«thyl)ether
Bls(2-chloroisopropyi)ether
Bls(2-ethythexyT)phthalate
Bromodlchloromemane
Bromoform
Bromomethane
Bfomodlphanyl ether, p-
Butanone. 2- (Methyl ethyl katone)
ButytbenzylphthaUte
Carbon dlsulflde
Carbon telrachlorlde
Chlordane
Chtoro-3-methylphenol. 4-
Chloroenlllne, p- (4-Chloroaniline)
Chlorobenzene
Chlorobanzllata
Chloroethane (Ethyl chloride)
Chloroform
f*t*lA»Ma<*AM« ••*•>,
ifnivionwinBnv
Chloronaphthalene. beta
Chlotophenol, 2-
Chlorodiphenyl ether. 4- \
Chrysone
Cresol, m-
Cresol. o- (2-Methylphenol)
Cresol, p-
Crotonaldehyde
Cumene
DOE, 4,4'-
Dibenz(a,h)anthracene
Dlbfomochloromethane
Dichlorobenzene. 1.3-
Dichlorobenzene. 1 .4-
Dichlorobenzene, 1,2-
Dichlorobenzidlne. 3,3'-
Dlchlorobiphenyl
Inhalation
Slope
Factor
(mg/k9-d)«-1
NA
NF
77E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
27E^>1
NA
81E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
0.07
0004375
NF
NA
004375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RIO
(mg/kg-d)
1 5E-02
NF
6 4E-04
2 5E-02
2 5E 02
1 4E-04
7 5E-02
43E-04
10E+00
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E03
50E-03
50E-03
36E-04
NA
7 IE 02
5 OE-02
7 1E-04
1 4E-04
1 5E-05
NF
106-03
1 4E-03
5 OE-03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E-02
1 3E 02
1 3E-03
NA
64E 04
NA
NA
5 OE-03
NA
5 7E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E-06
87E-06
30E-04
29E 03
2 9E 04
20E-04
55E-08
15E-05
1 IE-OS
32E^»
55E-06
55E-06
55E-08
5SE-06
55E-06
67E-08
13E-05
67E-OB
37E-05
10E-04
55E-OS
49E-04
67E-08
51E-05
55E-06
89E-05
16E-04
55E-07
87E-06
87E-06
55E-06
37E-05
49E-04
27E^)4
2 5E-04
67E-06
55E08
67E-06
55E06
55E06
55E 06
55E-06
1 4E 04
55E06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
N3max
N3 max
N3max
NSmax
N3max
N3max
NSmax
N3max
NSmax
N3m«x
N3max
NSmax
N3max
N3max
N3 max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3 max
NSmax
N3 max
NSmax
N3max
N3max
N3max
N3max
NSmax
NSmax
N3max
NSmax
NSmax
NSmax
NSmax
N3 max
NSmax
NSmax
NS max
NSmax
NS max
NSmax
N3 max
Adult
Cancer
Risk
NT
NT
31E-12
NT
NT
64E-11
NT
57E-13
NT
NT
NT
NT
NT
NT
NT
NT
20E-11
NT
NT
NT
28E-14
NT
NT
NT
NT
NT
1 1E-11
95E-13
NT
NT
NT
1 3E-11
NT
29E-11
21E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
77E-12
NT
NT
1 6E-10
NT
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
49E-11
NT
NT
NT
7.1E-14
NT
NT
NT
NT
NT
28E-11
2 4E-12
NT
NT
NT
33E-11
NT
7 IE 11
51E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
47E-12
NT
NT
97E-11
NT
86E-13
NT
NT
NT
NT
NT
NT
NT
NT
29E-11
NT
NT
NT
43E-14
NT
NT
NT
NT
NT
1 7E-11
1 4E-12
NT
NT
NT
20E-11
NT
43E-11
31E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
fIT
NT
NT
Farmer
Cancer
Risk
NT
NT
69E-12
NT
NT
1 4E-10
NT
1.3E-12
NT
NT
NT
NT
NT
NT
NT
NT
4.4E-1 1
NT
NT
NT
83E-14
NT
NT
NT
NT
NT
25E-11
21E-12
NT
NT
NT
30E-11
NT
64E-11
46E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                           Adult     Child    School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HO       HQ        HQ
46E-09
NT
49E06
1 2E-06
1 2E-07
1 5E-05
76E-10
3 6E-07
1 2E-10
NT
NT
NT
NT
NT
NT
NT
NT
70E-09
77E-08
2 1E-07
1 IE-OS
14E-OS
NT
7SE-09
1 1E-09
13E-06
12E05
38E-07
NT
7 OE-08
40E08
77E-08
71E-09
1 1E-06
NT
35E-09
4 6E-08
NT
NT
46E-09
46E-09
4 6E-08
NT
89E 08
NT
NT
5 5E 08
NT
1 OE 09
4 OE 09
tIT
m
1 7E-08
NT
1 BE -05
45E06
4 6E-07
55E05
29E-09
1 3E-06
44E-10
NT
NT
NT
NT
NT
NT
NT
NT
26E-08
29E07
80E-07
43E08
5.3E-05
NT
28E08
43E-09
49E-06
43E05
1.4E-06
NT
26E07
1 5E-07
2 9E-07
27E08
41E-06
NT
1 3E-08
1 7E-07
NT
NT
17E08
1 7E 08
1 7E 07
NT
3 3E 07
NT
NT
2 OF. 07
NT
3 7E 09
1 5E 08
NT
NT
1 OE-08
NT
1 IE-OS
27E06
2 8E-07
33E05
1 7E-09
8 IE 07
2 7E-10
Nt
NT
NT
NT
NT
NT
NT
NT
1 6E-08
1 7E-07
4 BE -07
2 6E 08
32E-05
NT
1 7E 08
26E-09
29E06
26E-05
86E-07
NT
1 6E 07
90E08
1 7E 07
16E08
25E06
NT
79E-09
1 OE-07
NT
NT
IDE 08
1 OE 08
1 OE 07
NT
20E07
NT
NT
1 7E 07
NT
23E 09
90E09
NT
n\
46E-09
NT
49E06
12E 06
1 2E-07
1 5E 05
76E 10
36E-07
1 2E-10
NT
NT
NT
NT
NT
NT
NT
NT
70E-09
7 7E 08
2 IE 07
1 IE 4)8
14E4W
NT
75EO9
1 IE 09
1 3E 36
12E05
38E-07
NT
70E08
40E 08
77E08
7 1E-09
1 IE -06
NT
35E-09
46E-08
NT
NT
46E 09
46E 09
4 6E-08
NT
89E-08
NT
NT
55E 08
NT
10E 09
40E 09
NT
tJT
Volume V. Appendix V-14
-------
?
oaniline. 3-






Z Z 2
-r » 2
lochlotobiphenyl
il.ttialene
oaniline. 2-






2 £
CB a
tiylene chloride
hylnaphttialen*. 2-






1
3f
•^
KJ
j
§
|
.w
S
CD
^




2Z S
9 A U
leic hydrazida
Ihoxychlor
Ihyl-t-butyl ether






8 i
Bno(t.2,3-cd)pyrene
jhorone






55
cachlorophena
canona, 2-
> f





55
ochforocyclopentadic
robiphenyl
•achlorobutadiene






maldehyde
foral
plachlor
ptachloroblphenyl
«achlorobenz«ne












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-------
TABLE 18  Maximum n.iialation Risks and Noncancel HQs in Subarea N3



CHEMICAL
Dichlorodrfluoromethane
Dlchlofoethane. 1 .1- (Ethylidene dichloride)
Dlchloroethane. 1,2-
Dichloroelhene. 1.1- (Vlnylidine chloride)
CMchloroettwne (bins). 1 .2-
Dlchlorophenol. 2.4-
Dfchloropropane. 1 .2- (Propylen* dichloride)
Dlchloropropene (els), 1 .3-
Dlchlofopf opene (bens), 1 ,3-
W^thylpntnalate
Dimethoxybenzidln*. 3.3'-
DfnwuiyfpnAnol, 2,4-
Dlmethylphthalate
CH n-bulylphthalate
DlnKrotoluene. 2,6-
tMnHro-2-nwttiyiphenof. 4.6-
Dtnttrophenol, 2,4-
CHnttrotofuene. 2.4-
Dtoxan*, 1 .4-
Dt(n)ody) phthalata
D. 2.4-
Elhyl melhecrylate
EtfHbenzane
Etnyfene dlbromrde
Ethylene oxide
Ethylene thlourea
Fluotanthene
FltKxene
Formaldehyde,
Furfural
Heptachtof
Heptachloroblphenyl
Hexachlorobenzene
Hexaebloroblphenyl
Hexachlorobutadien*
Hexechlorocyctohexane. gtmma (Llndane)
Hexachtorocyclopentadlen*
Hexachloroeihine ':
Hexachlorophene
Hexanone, 2-
lndeno(1 ,2,3-cd)pyrene
Isophorone
Malelc hydrukto
Methoxychlor
Methyl 1 butyl ether
Methyl-2-Pentanone, 4- (MIBK)
Methylene chloride
Methylnaphthalene, 2-
Monochlorobiphenyl
Naphthalene
Nrt/oaniline. 2-
Nitroanihne. 3-
Inhalation
Slope
Factor
(mg/kg-d)A-1
NA
MA
91E-02
1 2E+00
NA
NA
NA
1 3E-01
1.3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E^>1
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
16E+00
NA
78E-02
NA
NA
14E-0?
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF
NA
NA -
NA
NF


RAC
(mg/m3)
DOS
0125
NA
0 007875
00175
0 002625
0001
0005
0005
07
NA
00t75
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
075
002
075
NF
NA
0035
000005
NF

Inhalation
RID
(mg/kg-d)
1 4E-02
36E-02
NA
23E-03
SOE-03
7 5E-04
29E-04
1 4E-03
1 4E-03
20E-01
NA
50E-03
NA
25E02
25E-04
NF
50E-04
50E-04
NA
50E-03
25E4J3
23E-02
7 1E-02
1 4E-05
NA
20E-05
10E-02
IDE -02
50E-02
36E-03
1 3E-04
NA
20E-04
NA
50E-05
75E-05
50E-06
25E-04
75E-05
NF
NA
5 OE 02
1 3E 01
1 3E-03
2 IE 01
5 7E 03
2 1E-01
NF
NA
1 OE 02
1 4E 05
NF

Emission
Rate
(g/sec)
25E-04
3E-05
3E-05
3E-05
3E05
5E-06
3E-05
.3E-05
3E05
7E-05
2E04
55E-06
55E-06
16E-05
55E-06
55EXW
55E-06
55E^W
49E-04
55E-06
39E-05
25E-04
50E04
1 2E-04
3 IE-OS
1 5E-10
55E-06
67E-06
61E4M
55E-06
5 5E-07
1 4E-08
55E-06
14E-08
1 OE-04
55E-05
55E-06
S5E-06
32E-05
64E-05
55E-06
67E-06
1 2E-04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
67E 06



Subarea
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
NSmax
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3 max
N3 max
N3max
N3max
N3max
N3max
N3max
N3m*x
N3max
N3max
N3max
N3max
N3max
N3ma«
N3 ma«
N3max
N3 max
N3 max
N3 max
N3max
N3 max
N3max
N3 max

Adult
Cancer
Risk
NT
NT
1 5E-12
20E-11
NT
NT
NT
22E-12
22E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-10
1 4E-11
NT
NT
NT
37E-11
NT
33E-12
NT
12E-11
NT
1 1E-11
NT
NT
1 OE-13
NT
NT
NT
NT
NT
NT
NT
NT
8 7E 13
NT
NT
NT
NT
NT

Child
Cancer
Risk
NT
NT
3BE-12
50E-11
NT
NT
NT
54E-12
54E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
29E-10
36E-11
NT
NT
NT
91E-11
NT
82E-12
NT
30E-11
NT
26E-11
NT
NT
26E-13
NT
NT
NT
NT
NT
NT
NT
NT
2 2E 12
NT
tJI
NT
m
NT

School-age
Cancer
Risk
NT
NT
23E 12
30E-11
NT
NT
NT
33E-12
33E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
22E-11
NT
NT
NT
55E-11
NT
50E-12
NT
1 8E-11
NT
1 6E-11
NT
NT
16E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 12
NT
nr
NT
NT
NT

Farmei
Cancer
Risk
NT
NT
34E 12
45E-11
NT
NT
NT
48E-12
48E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E-10
32E-11
NT
NT
NT
81E-11
NT
74E-12
NT
2 6E-1 1
NT
23E-11
NT
NT
23E-13
NT
NT
NT
NT
NT
NT
NT
m
1 9E 12
NT
tJT
fIT
NT
NT
                                                                                                                                             Adult      Child   School-age   Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ       HQ       HQ       HQ
1 BE -07
36E-09
NT
5BE-08
26E-08
76E-08
4 6E-07
91E-08
91E-08
8 8E-10
NT
1 IE-OS
NT
65E-09
23E-07
NT
1 1E-07
1 1E-07
NT
1 1E-08
1 6E-07
1 1E-07
73E-08
84E-05
NT
76E 11
57E-09
70E09
1 3E 07
16E08
46E-08
NT
2 9E-07
NT
21E-05
76E-06
1 1E-05
2 3E-07
44E-06
NT
NT
1 4E 09
96E-09
46E09
6 IE 10
2 3E 08
1 9E 08
NT
NT
5 7E 09
49E 06
NT
6 7E-07
1 4E-08
NT
22E-07
9 7E-08
2 9E-07
1 7E-06
34E-07
3 4E-07
33E-09
NT
43E-08
NT
2 4E-08
86E-07
NT
4 3E-07
43E-07
NT
43E-08
60E-07
42E-07
27E4J7
31E-04
NT
28E 10
2 IE-OS
26E08
4 7E 07
60E-08
1 7E-07
NT
1 1E-06
NT
79E-05
2 BE 05
43E-05
86E07
1 7E-05
NT
NT
52E-09
36E 08
1 7E 08
23F 09
BSE 08
7 2F. 08
NT
NT
2 IE 08
1 8F 05
NT
4 OE-07
82E-09
NT
1 3E-07
59E-08
1 7E-07
10E06
2 IE 07
21E-07
20E-09
NT
26E08
NT
1 5E 08
52E-07
NT
2 6E-07
26E-07
NT
26E-08
36E-07
26E-07
1 6E 07
19E04
NT
1 7E 10
13E08
16E-08
2 9E 07
36E-08
1 OE-07
NT
6 5E-07
NT
4 7E 05
1 7E 05
26E05
52E 07
1 OE-05
NT
NT
3 IE 09
22E08
1 OE 08
1 IE 09
5 IE 08
4 3E 08
NT
NT
1 3E 08
1 IE 05
NT
1 BE -07
36E-09
NT
5 BE -08
2 6E-08
76E08
46E07
91E-08
9 IE-OS
88E-10
NT
1 IE-OS
NT
65E09
2.3E-07
NT
1E-07
IE-07
NT
IE-OS
6E-07
IE 07
73E-08
8 4E-05
NT
76E-11
57E09
70E09
1 3E 07
16E 08
46E-OB
NT
2 9E-07
NT
2 IE 05
76E06
1 IE-OS
2 3E 07
44E-00
NT
NT
1 4E 09
96E09
46E09
6 IE 10
23E 08
1 9E-08
NT
NT
57E 09
49E 06
NT
Volume V. Appendix V-14
-------
TABLE 18  Maximum Inhalation Ri^ks and Noncancer HQs in Subaiea N3
CHEMICAL
Nrtroanlline, 4-
Nitrobenzene
Nibophenol. 2-
Nfaophenol, 4-
N Nttroso-di-n-butylamlna
N-Nttroso-di-n-propylamina
N-NKiosodlphanylamlne (Diphenylamlne)
Nonachlorobiphenyt
Ociachlofobiphenyi
Pant»chk>rob«rurena
Pentachlorobiphenyl
Pentachloronltrobenzene
Pantachlorophanol
Ph«nanthr«n«
Phenol
Pyr«n«
Safrok* (5-(2-Propenyl)-1,3 benzodioxole)
Styran*
T elrachloroblphenyl
Telrachloroethane. 1 1.1.2
Tetrachloroethane. 1.1.2.2-
Tetrachloroethene
Tebachlorophenol. 2.3.4.6
Toluana
TrrchrofO-1.2,2.brfluoroethane. 1.1.2-
Trichlofob«ruana, 1.2.4
Trichloiobiph»ny1
Trlchloroethana, 1 . 1 . 1 - (Methyl chloroform)
Trlchlofoathana. 1,1.2
Trlchtoroethene
T rlchtof oAuoiomathane
Trichtorophenol. 2.4.5-
Trlchtorophonol. 2.4,6-
Vinyl acetate
Vinyl chlotida
Xylena. m/p- (m/p-Dlmethyl beruene)
Xylene. o- (o-Dimethyl benzene)
2,3.7.8-TCDD '
1. 2.3.7.8 PCDD
1 .2.3,4 7.8 HxCDD
t. 2,3,6.7.8 HxCOO
12 3, 7,8 9 HxCDD
1.2,3,46.7.8 HpCDD
DCDD
J.3.7.8-TCDF
1 2 3 7 8 PCDF
1 3 4 7.8 PCDF
1 2.3.4.7.8 HxCDF
1236 7.8H«COF
? 3 4 6 7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg d)"-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E^)2
2 OE-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E-02
60E^)3
NA
NA
1 OE-02
NA
3 OE-01
NA
NA
1 5E+05
75E*04
5E»04
5E»04
5E+04
5E*03
5E»02
1 5E*04
75E»03
75E»04
1 5E»04
t 5E»04
1 5E*04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
HA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E 04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E 01
7 5E-03
NF
7 1E-02
NA
75E-03
NA
25E 03
7 5E 03
29E 02
2 1E»00
1 4E 02
NA
7 1E 02
10E 03
NA
50E02
2 5E-02
NA
1 4E 02
NA
5 OE-01
5 OE-01
NA
NA
NA
NA
NA
NA
HA
NA
NA
NA
II A
NA
NA
Emission
Rate
(g'sec)
6 7E 06
55E 06
67E-06
55E06
1 2E 04
67E 06
67E-06
14E-08
1 4E-00
' 48E 05
1 4E-08
34E-05
55E-08
67E-06
55E06
55E-06
1 2E-04
23E 05
1 4E 08
55E-06
55E 06
5 IE-OS
69E 06
6 IE 04
3 3E 04
55E-06
30E 08
1 3E-05
1 3E 05
1 9E-05
2 5E-04
55E-06
55E-06
64E 05
2 5E-04
38E 04
55E-06
1 08E 11
678E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
46?E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3 max
N3max
N3max
N3 max
N3 max
N3max
N3max
N3 max
N3max
N3max
N3max
N3 max
N3max
N3max
N3 max
N3max
N3max
N3 max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3 max
N3max
N3max
N3max
N3 max
N3max
N3max
N3 max
N3 max
N3max
N3max
H3 max
N3 max
N3 max
N3mai
IJ3 max
N3 max
N3 max
Ofl site
Vapoi
Cone
(ug/m3)
25E 07
2 1E 07
25E 07
2 IE 07
46E06
25E 07
2 5E-07
53E-10
53E 10
1 8E-06
53E-tO
1 3E-06
2 IE 07
2 5E-07
2 1E-07
2 1E-07
44E 06
86E-07
53E 10
2 IE 07
2 1E-07
1 9E 06
26E^)7
23E 05
1 3E 05
2 1E-07
1 1E-09
4 8E-07
4 BE 07
7 IE 07
93E 06
2 IE 07
2 1E 07
24E 06
93E-06
1 4E-05
2 1E 07
4 1E 13
26E 12
34E 12
63E 12
4 IE 12
4 7E 11
2 3E 10
3 3E 12
1 3E 11
1 8E 11
5 4E 11
5 IE 11
5 7E 11
Cancer
Adult
Dose
(mg/Kg-d)
90E 12
74E-12
90E 12
74E-12
1 6E-10
90E-12
90E 12
1 9E-14
1 9E-14
64E 11
1 9E-14
45E-U
74E-12
90E-12
74E-12
74E-12
1 5E-10
30E-11
1 9E-14
74E-12
74E-12
69E-11
9 IE 12
82E 10
44E-10
74E-12
40E-14
1 7E-11
1 7E-11
25E-11
33E-10
74E-12
74E-12
86E-11
33E-10
5 1E-10
74E-12
1 4E-17
9 IE 17
1 2E 16
22E 16
1 5E 16
1 7E 15
62E 15
1 2E 16
46E 16
6 21 16
1 9E 15
1 BE 15
7 OE 15
Cancer
Child
Dose
(mg/kg-d)
2 2E-11
1 BE 11
22E-11
1 BE 11
40E 10
22E 11
22E 11
47E 14
4 7E-14
16E 10
47E-14
1 1E-10
1 8E-11
22E-11
1 8E-11
1 8E-11
38E-10
75E-11
47E 14
8E-11
BE- 11
7E-10
3E 11
OE-09
1E-09
BE 11
OE-13
42E-11
42E-11
62E-11
82E-10
1 8E-11
1 BE 11
2 1E-10
82E 10
1 3E-09
1 8E-11
36E 17
23E 16
30E 16
55E 16
36E 16
4 IE 15
20E 14
2 9E 16
1 IE 15
1 6F 15
4 BE 15
44E 15
•5 OF 15
Cancer
School age
Dose
(mg/kg-d)
1 3E 11
1 IE 11
1 3E-11
1 1E-11
24E-10
1 3E 11
1 3E-11
28E-14
2 BE 14
96E-11
2BE-14
68E-11
1 IE-It
t 3E-11
1 1E-11
1 1E-11
23E-10
45E-11
2 BE 14
1 1E-11
1 1E-11
1 OE-10
1 4E-11
1 2E-09
66E-10
1 1E-1I
61E-14
25E 11
25E 11
3BE-11
49E 10
1 1E-11
1 1E-11
1 3E-10
49E-10
77E 10
1 1E-11
22E 17
1 4E 16
1 BE 16
33E 16
22E 16
25E 15
1 2E 14
1 8E 16
69E 16
94E 16
29E 15
2 7E 15
3 OF 15
Cancer
Farmer
Dose
(mg/kg-d)
20E-11
1 6E-11
20E 11
16E 11
36E 10
20E 11
20E It
42E-14
42E-14
1 4E-10
42E 14
10E-10
16E-11
20E 11
16E 11
1 6E-11
34E-10
67E-11
42E-14
t 6E-11
1 6E-11
1 5E 10
20E 11
1 8E-09
98E-10
16E-11
90E-14
37E 11
37E-11
55E 11
73E-10
16E-11
1 6E-11
1 9E-10
73E-10
1 1E-09
16E-11
32E-17
20E 16
27E 16
49E-16
32E 16
3 7E 15
1 BE 14
76E 16
t OE 15
1 4E 15
4 2E 15
4 OF 15
4 ',f 15
Noncancer
Adult
Dose
(mg/kg-d)
70E 11
57E 11
70E 11
57E 11
13E09
70E 11
70E-11
15E-13
15E-13
50E-10
15E-13
35E 10
57E-11
70E-11
57E-11
57E It
1 2E-09
23E-10
1 5E-13
57E 11
57E 11
53E 10
7 IE 11
64E09
34E 09
57E 11
31E-13
t 3E 10
t 3E 10
1 9E 10
25E^)9
57E-11
57E-11
67E-10
25EO9
4 OE-09
57E-11
1 1E-16
7 IE 16
93E 16
1 7E 15
1 IE 15
t 3E 14
64E 14
9 IE 16
36E 15
49E 15
1 5f. 14
1 4F 14
1 6F M
Noncancer
Child
Dose
(mg/kg-d)
26E 10
2 IE 10
26E 10
21E 10
4 7E 09
26E-10
26E 10
54E-13
54E-13
19E-09
54E 13
1 3E-09
2 IE 10
26E-10
2 IE 10
21E 10
4 5E 09
87E-10
54E 13
2 1E-10
2 IE tO
2 OE-09
26E 10
24E-08
1 3E-08
2 IE 10
1 2E 12
49E-10
49E 10
72E 10
9 5E 09
2 1E-10
2 IE 10
25E09
95E 09
1 5E 08
2 IE 10
42E 16
26E 15
35E 15
64E 15
4 ?E 15
4 BE 14
2 4E 13
34F 15
1 Jt 14
1 BF 14
SSf. 14
5?C 14
5 9f 14
Moncancer
School-age
Dose
(mg/kg-d)
1 6E 10
1 3E 10
16E 10
1 3E-10
28E 09
1 6E 10
1 6E 10
33E 13
33E 13
1 IE 09
33E-13
79E 10
1 3E-10
1 6E-10
1 3E-10
1 3E 10
27E-09
53E 10
33E-13
1 3E 10
1 3E 10
1 2E09
1 6E 10
1 4E^)8
78E^)9
1 3E 10
7 IE 13
29E 10
29E 10
44E 10
56EOT
1 3E 10
1 3E-10
15E 09
5 BE 09
89E 09
1 3E 10
25E 16
1 6E 15
2 1E 15
39E 15
26E 15
29E 14
1 4E 13
2 IE 15
8 IE 15
1 IE 14
34E 14
3 IE 14
35F 14
Noncancer
Farmer
Dose
(mg/kg-d)
70E-11
57E 11
70E 11
57E-11
1 3E-09
70E 11
70E 11
15E-13
15E 13
50E 10
1 5E 13
35E 10
57E-11
70E-11
57E-11
57E-11
1 2E-09
23E-10
15E-13
57E-11
57E 11
53E 10
7 IE 11
64E09
34E09
57E 11
3 IE 13
1 3E-tO
1 3E-10
19E 10
25EX»
57E tl
57E-11
67E 10
25E09
40E 09
57E-11
1 IE 16
7 1E 16
93E 16
1 7E 15
1 IE 15
1 3E 14
64E 14
9 IE 16
36E 15
49E 15
1 5E 14
1 4E 14
1 RF 14
 'olume V. Appendix V 14
-------
TABLE  18  Maximum^   .alion Risks and Noncancer HQs in Subatea N3
CHEMICAL
Htttoanlline. 4-
Nitrobenzene
Nitrophenol. 2
Nitrophenol. 4
N NHroso-dl-n-butytamlne
N-Nitroso-di-n-propylamine
N-NHrosodlphenytamlne (Diphenylamine)
Nonachloroblphanyl
OctochloroMphenyl
Pentachtorobenzene
Pentachloroblphenyl
PentachroionHrobenzene
Pentachtorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl)-1.3-benzodloxole)
Styrene
Tetrachlorobiphenyl
Tetrachloroelnane. 1.1.1,2-
Tetrachloroethane. 1.1.2.2-
T etrachkxoethene
Tetrachlorophenol. 2.3.4,6-
Toluene
Trichloro-1.2.2-trHluoroethane. 1.1.2-
Trlchlorobenzene, 1.2,4-
Trtchtoroblphenyl
Trichlofoethane. 1.1,1- (Methyl chloroform)
Trlchloroethane, 1.1,2-
Trichloroethene
Trrchtoroftuoromefftarw
Trichlorophenol. 2,4,5-
Trichlorophenol, 2.4.6-
Vinyl acetate
Vlnyt chloride
Xylene, m/p- (m/p-Dlmethyl benzene)
Xylene, o- (o-Dimethyl benzene)
2.3,7,8-TCDO
1.2.3,7.8-PCDD
1,2.3,4,7,8 HxCDO
12367 B-HxCDD
1.2.3.7,8.9-HxCDD
1.2,3,4,6.7,8-HpCDD
OCDD
2.3.7.8-TCDF
1.2,3.7.8-PCDF
2.3.4. 7.8-PCDF
1.2 3.4.7.8 HxCDF
1.2.3.6. 7.8 HxCDF
2.3.4.6.7.8 HxCDF
Inhalation
Slope
Factor
(mg/kg-d)*-1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 BE -02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E-02
60E-03
NA
NA
10E-02
NA
30E-01
NA
NA
15E+05
7 5E404
5E*04
5E+04
5E+04
5E+03
5E»02
5E«04
5E«03.
5E*04
5E»04
5E*04
5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
002625
NA
OS2S
0 02625
NF
025
NA
002625
NA
000875
0 02625
0 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
HA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
7 5E-03
NF
7 1E-02
NA
75E-03
NA
25E-03
7 5E-03
2 BE -02
2 1E+00
1 4E-02
NA
7 1E-02
1 OE-03
NA
5 OE 02
25E-02
NA
1 4E-02
NA
50E-01
50E-01
NA
NA
NA
NA
NA
HA
HA
NA
HA
HA
HA
HA
HA
Emission
Rate
(g/sec)
67EO6
55E 06
67E-06
55E-06
1 2E-04
67E06
67E-06
1 4E-08
1 4E-08
4 BE -05
1 4EO8
34E-05
55E06
67E-06
55E-06
55E06
1 2E-04
23E-05
1 4E 08
55E-08
55E06
S1E-05
6 BE -06
61E-04
33E-04
55E-06
30E 08
13E05
13E-05
1 9E 05
25E-04
55E06
55E06
64E-05
2 5E-04
3 BE -04
55E-06
1 OBE-11
67BE 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
N3max
N3 max
N3max
N3max
N3max
N3max
N3 max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3 max
N3max
N3max
N3max
N3max
N3mw
N3max
N3m*x
N3 max
N3max
N3 max
N3max
N3 max
N3max
N3max
N3max
N3max
N3 max
N3max
N3 max
N3max
N3max
N3 max
N3max
N3max
H3 max
N3ma
H3ma
H3ma
H3ma
143 ma
H3ma
143 ma
H3ma
143 ma
Adult
Cancer
Risk
NT
NT
NT
NT
8 7E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 9E-13
1 5E 12
1 4E-13
NT
NT
NT
NT
NT
NT
95E-13
1 5E-13
NT
NT
74E-14
NT
9 BE 11
NT
NT
22E 12
6BE 12
1 BE 12
33E 12
22E 12
25E 12
1 2E 12
1 BE 12
3SE 12
4 7E 11
29E 11
2 7E 11
30E 11
Child
Cancer
Risk
NT
NT
NT
NT
22E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 7E-13
37E-12
35E-13
NT
NT
NT
NT
NT
NT
24E-12
37E-13
NT
NT
1 8E-13
NT
24E 10
NT
NT
54E-12
1 7E 11
45E 12
83E 12
54E 12
62E 12
3 1E 12
44E 12
86E 12
1 2E 10
7 IE 11
6 7E 11
75E 11
School-age
Cancer
Risk
NT
NT
NT
NT
1 3E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
29E-13
22E-12
2 1E-13
NT
NT
NT
NT
NT
NT
1 4E-12
22E-13
NT
NT
1 1E-13
NT
1 5E-10
NT
NT
33E 12
1 OE 11
27E 12
50E 12
33E 12
3 7E 12
1 9E 12
26E 12
5 2E 12
70E 11
4 3E 11
40E 11
45E 11
Farmer
Cancer
Risk
NT
NT
NT
NT
19E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
42E-13
33E-12
3 1E-13
NT
NT
NT
NT
NT
NT
2 IE 12
33E-13
NT
NT
1 6E-13
NT
22E-10
NT
NT
48E-12
1 5E 11
40E 12
74E 12
49E 12
55E 12
2 7E 12
39E 12
7 7E 12
1 OE 10
64E 11
6 OF 11
6 7E II
                                                                                                                                           Adult      Child   School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HQ       HQ       HQ
NT
4 OE-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 7E-07
76E-09
NT
38E-10
76E-09
NT
33E-09
NT
76E-09
NT
2 1E-07
94E-09
2 2E 07
16E-09
40E-09
NT
16E09
1 3E-07
NT
5 IE-OB
23E-09
NT
47E-08
NT
79E-09
1 IE 10
NT
NT
NT
NT
NT
NT
HI
NT
HI
HI
HT
UT
III
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-06
29E08
NT
14E-09
29E-08
NT
1 2E-08
NT
29E-08
NT
6 OE-07
35E-08
8 3E-07
80E-09
15E-08
NT
6 BE 09
49E-07
NT
1 9E 07
86E-09
NT
1 BE -07
NT
30E08
43E 10
NT
NT
NT
HI
Ml
HI
HI
HI
III
III
fit
HT
HI
NT
9 OE-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-06
1 7E-08
NT
86E-IO
17E-08
NT
74E-09
NT
1 7E-08
NT
4 BE 4)7
2 IE-OS
5 OE-07
36E09
90E-09
NT
41E09
29E-07
NT
1 2E-07
52E-09
NT
1 1E-07
NT
1 BE 08
26E 10
MT
HT
HT
NT
HT
fIT
HT
HI
HT
HT
HI
NT
HT
NT
4 OE-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 7E-07
76E-09
NT
38E-10
76E-09
NT
33E-09
NT
76E-09
NT
2 IE 07
94E-09
2 2E 07
16E09
40E-09
NT
1BE09
1 3E-07
NT
5 IE-OB
23E-09
NT
4 7E-08
NT
79E-09
1 1E-10
NT
NT
NT
HT
NT
NT
HI
HI
HI
HT
NT
HI
HT
Volume V. Appendix V-14
-------
TABLE 18  Maximum Inhalation Risks and Noncancfr HQs in Subacea N3
CHEMICAL
1.2 3.7.8.9 HxCDF
1 2.3.4.6. 7.8 HpCDF
1,2.3.4.7.8.9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Respirable particulars
Inhalation
Slope
Factor
(mg/kg-d)*-1
1 5E*04
15E*03
t 5E»03
1 5E+02

NA
NA
50
NA
84
6 1
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0 004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg d)
NA
NA
NA
NA

NA
1 OE-04 •
75E-05
36E05
1 3E 03
1 3E 04
1 3E 03
2 5E-01
NA
NA
2 1E 05
50E03
1 3E 03
1 3E 03
1 8E 05
7 5E 02
50E 04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E 10
930E 09
t 22E 09
1 89E 08
4 28E 08
24E04
42E-06
37E-05
15E 04
33E 08
16E4I5
71E47
71E^)7
94E05
43EXB
1 4EX)3
506^8
47E^>4
1 5EX»
34E05
1 2E 04
32E^)2
24E*00
9 1E42
72EXJ2
72E4J2
Subarea
N3m*x
N3 max
N3 max
N3 max

N3max
N3max
N3 max
N3 max
N3 max
N3max
N3max
N3 max
N3max
N3 max
N3 max
NSmex
N3max
N3 max
N3max
N3max
N3max
NSmax
N3max
N3max
N3max
Off site
Vapoi
Cone
(ug/mJ)
1 IE 11
35E 10
46E 11
72E-10

9 IE 06
1 6E-07
1 4E-06
57E 06
1 3E-09
6 1E-07
27E08
27E^>8
36E 06
t 6E 06
53E-05
1 9E-07
1 BE 05
57E07
1 3E 06
46E-O6
t 2E-03
92E 02
35E03
2 7E 03
2 7£ 03
Cancer
Adult
Dose
(mg/kg d)
39E 16
1 2E 14
1 6E 15
25E 14
57E 14
32E 10
56E 12
50E 11
20E 10
44E 14
2 1E-11
9SE 13
95E 13
1 3E 10
5 BE It
1 9E-09
6TE 12
63E-10
20E 11
45E-11
1 6E-10
43E-08
32E-06
1 2E 07
96E 08
96E-08
Cancer
Child
Dose
(mg/kg d)
98E 16
3 1E 14
4 IE 15
63E 14
1 4E 13
80E-10
1 4E 11
1 2E 10
50E 10
1 IE 13
53E-11
24E-12
24E-I2
31E 10
1 4E-10
47E 09
1 7E-11
1 6E-09
50E-11
1 1E-10
40E-10
1 1E-07
81E-06
30E07
2 4E 07
2 4E-07
Cancer
School-age
Dose
(mg/kg-d)
59E-16
1 9E 14
25E 15
38E 14
86E 14
48E-10
BSE 12
75E-11
30E-10
66E 14
32E-11
1 4E-12
1 4E-12
19E-10
87E-11
28E-09
10E-11
95E 10
30E-11
6BE-11
24E-10
64E08
49E-06
1 BE 47
1 5E 07
t 5E-07
Cancer
Farmer
Dose
(mg/kg-d)
B7E 16
28E-14
36E-15
56E 14
1 3E 13
7 IE 10
1 2E-11
1 IE 10
45E 10
98E-14
48E-11
2 IE 12
2 IE 12
28E-10
1 3E-10
42E-09
1 5E-11
1 4E 09
45E 11
1 OE-10
36E-10
95E-08
72E-06
27Efl7
2 1E-07
2 1E-07
Noncancer
Adult
Dose
(mg/kg-d)
30E 15
9 7E 14
1 3E 14
20E 13
44E-13
25E09
44E-11
39E-10
16E09
34E-13
1 7E 10
74E-12
74E-12
96E-10
45E-10
1 5E-08
52E-11
49E-09
16E 10
35E-10
1 2E-09
33E4)7
25EX«
9 5E-07
7 5E 07
7 5E-07
Noncancer
Child
Dose
(mg/kg-d)
1 1E-14
36E 13
47E-14
74E 13
1 7E-12
93E49
1 6E-10
1 4E-09
5 BE -09
1 3E-12
62E-10
2BE-11
2 BE 11
37E-09
1 7E-09
54E-08
1 9E-10
18E-08
58E-10
1 3E-09
47E-09
1 2E-06
94E«5
35E-06
2 BE 06
28E-06
Noncancer
School age
Dose
(mg/kgd)
69E 15
22E 13
29E 14
45E 13
10E 12
56E 09
99E 11
B7E 10
35E09
78E-13
36E-10
1 7E 11
1 7E-11
22E^»
10E 09
3 3E 08
12E 10
1 IE-OB
35E 10
8 OE-10
2 BE -09
75E 07
57E 05
2 1E 06
1 7E 06
1 7E 06
Noncancer
Farmer
Dose
(mg/kg d)
30E-15
9 7E 14
1 3E 14
20E 13
44E-13
25E^)9
44E-11
39E-10
1 6E 09
34E-13
1 7E-10
74E-12
74E-12
9 BE 10
45E-10
1 5E-08
52E 11
49E-09
1 6E 10
35E-10
1 2E-09
33E^)7
25E^)5
95E-07
75E4)7
75E^)7
NOTES:
  NA • No! applicable
  NF » Not found
  NT • No toxicrty informabon
  HQ * Hazard quotient
  HI = Hazard index
/olume V, Appendix V-14
-------
TABLE 18  Maximu
                mv.
nation Risks and Noncancet HQs in Subarea N3
CHEMICAL
1.2.3.7.8.9-HKCDF
1,2.3.4.6.7.6-HpCDF
1,2.3.47.8.9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivatont)
Copper
Lead
Mercury (and MeHg)
Nickel
Sttonnjni
SHver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Resplrabto participates
Inhalation
Slope
Factor
(mp/kg-d)«-1
1 5E+04
1 5E+03
15E*03
t 5E+02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0675
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
, NA
NA

NA
IDE -04
75E-05
36E-OS
13E-03
13E-04
13E-03
25E-01
NA
NA
2 IE-OS
50E03
13E-03
1 3E-03
18EO5
75E 02
SOE-04
NA
NA
NA
NF
Emission
Rate
(B/sec)
293E-10
930E-09
122E^»
1 69E-06
426E-08
24E-O4
42E-06
37E^«
15E-04
33E-06
16E4J5
71E^>7
7 1E-07
94E-OS
43E-05
14E4J3
50E-08
47E4M
15EX»
34E^»
1 2E-04
32E42
24E+00
91E-02
7 2E 02
72E-02
Subarea
N3 max
N3max
N3max
N3max

N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3max
N3mu
N3max
N3max
N3max
Adult
Cancer
Risk
59E-12
19E-11
25E 12
38E-12
19E-10
NT
NT
25E-09
NT
3 7E-13
13E-10
39E-11
NT
NT
NT
NT
56E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
1 5E-11
47E-11
61E-12
95E-12
47E-10
NT
NT
62E-09
NT
92E-13
33E-10
97E-11
NT
NT
NT
NT
1 4E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
89E-12
28E-11
37E-12
57E-12
28E-10
NT
NT
37E-09
NT
56E-13
20E-10
59E-11
NT
NT
NT
NT
65E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
1 3E-11
41E-11
54E-12
85E-12
42E-10
NT
NT
55E-09
NT
82E-13
29E-10
8.7E-11
NT
NT
NT
NT
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                            Adult     Child    School-age  Farmer
                                                                                                                                         Noncancer Noncancer Noncancer Noncancer
                                                                                                                                            HQ       HQ       HO       HQ
NT
NT
NT
NT
NT
NT
44E-07
51E-06
44E-OS
2 7E-10
13E-06
59E-09
30E-11
NT
NT
66E-04
1 OE 08
39E-06
1 2E-07
20E-05
1 7E-06
67E-04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1.6E-06
19E05
1 6E-04
10E-09
50E-06
22E08
1.1E-10
NT
NT
2 5E-03
39E08
15E-OS
47E^)7
76E05
62E-08
25E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
99E-07
12E-05
99E-05
6 2E-10
30E46
13E48
6.7E-11
NT
NT
15E-03
23E-06
6 BE -06
28E-07
46E-05
38E-08
15E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 4E 07
S1E-06
44E45
27E 10
1 3E-06
59E09
30E-11
NT
NT
6 BE 04
IDE -08
39E-06
12E4)7
20E-05
1 7E 08
67E-04
NT
NT
NT
NT
                                                                              Total Risk   42E-09   1OE-08   63E-09   93E-09
                                                                                                                                  Total HI   16E-03   60E-03   36E-03    16E-03
NOTES:
  NA-Not applicable
  NF-Not found      ':
  NT - No toxicrty fnformatlon
  HQ " Hazard quotient
  HI -HazardIndex
Volume V. Appendix V-14
-------
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-------
TABLE 19  Maximum V. nation Risks and Noncancet HQs m Subarea SI
CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
AcrylonHrile
Anthracene)
Benzene
Benzole acid
Benzotolchlortde
Benzo(a)anlhracene
Benzo(a)pyrene
Berxo(b)fluoranthene
B*nzo(g.h.l)p«fylene
Benzo(k)fluoranthene
Bls(2-chloioethoxy) methane
Bls(2-chk>roalhyi)ether
Bls(2-chloroisopropyl)ether
Bls(2-ethylhe)tyl)phthalate
Bromodlchloromethane
Bromoform
Bromomethane
Bromodlphenyl ether, p-
Butanone, 2- (Methyl ethyl kelone)
Butylbenzylphthalate
Carbon dlsulflde
Carbon tetrachloride
Chtordane
Chloro-3-methytphenol. 4-
Chloroaniline, p- (4-Chloroanillne)
Chlorobenzene
Chlorobanzllate
Chloroethane (Ethyl chloride)
Chloroform
Chloromettiane
Chtoronaphthalene, beta
Chlorophenol, 2-
Chlorodlphenyl ether. 4- ^
Chrysene
Cresol. m-
Cresol. o- (2-Methylphenol)
Cresol. p-
Crotonaldehyde
Cumene
DDE.4.41-
Dibenz (a ,h)anthracene
Dibromochloromethana
Dichlorobenzene. 1.3
Dichlorobenzene. 1 ,4-
Dlchlorobenzene. 1 .2-
Dkhlorobenzidine. 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/Vg-d)*-1
NA
NF
7 7E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
27E-01
NA
8 1E-02
6 3E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
3.5
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
0 04375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RfD
(mg/kg-d)
t 5E-02
NF
6 4E-04
2 5E-02
2 5E-02
1 4E-04
7 5E 02
43E-04
106+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE-02
5 OE 03
50E-03
50E-03
36E-04
NA
7 1E-02
50E02
7 IE 04
1 4E-04
1 5E-O5
NF
1 OE 03
14E-03
50E03
71E-01
25E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E-03
NA
64E04
NA
NA
50E 03
NA
57E 02
1 4E 02
NA
NA
Emission
Rate
(g/sec)
67E-06
67E-06
3 OE-04
29E 03
2 9E-04
2 OE-04
55E06
15E-05
1 IE-OS
32E48
S5E-06
55E-06
55E-06
55E06
55E-06
6 7E-06
1 3E-05
87E-06
37E4K
1 OE-04
55E46
4 9E-04
67E-06
SIE^rS
55E-08
6 9E-OS
16E-04
55E07
67E-06
67E-06
55E-06
37E-05
49E-04
27E-04
2 5E 04
67E-06
55E-06
67E-06
55E-06
55E-06
55E-06
55E-06
1 4E 04
55E06
55E 07
55E 06
26E 05
55E 06
55E06
55E 06
33E 05
4 7E 08
Subarea
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
S1 max
SI max
SI max
S1 max
SI max
SI max
SI max
St max
SI max
SI max
SI max
S1 max
SI max
SI max
St max
SI max
SI max
SI max
SI max
S1 max
SI max
SI max
SI max
SI max
St max
S1 max
SI max
SI max
SI max
SI max
SI max
St max
SI max
St max
SI max
SI max
Adult
Cancer
Risk
NT
NT
42E-11
NT
NT
86E-10
NT
7.7E-12
NT
NT
NT
NT
NT
NT
NT
NT
26E-10
NT
NT
NT
38E-13
NT
NT
NT
NT
NT
1 5E-10
1 3E-1 1
NT
NT
NT
1 8E-10
NT
38E-10
28E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
10E-10
NT
NT
22E-09
NT
19E-11
NT
NT
NT
NT
NT
NT
NT
NT
65E-10
NT
NT
NT
95E-13
NT
NT
NT
NT
NT
37E-10
32E-11
NT
NT
NT
45E-10
NT
96E 10
69E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
63E-11
NT
NT
1 3E-09
NT
12E-11
NT
NT
NT
NT
NT
NT
NT
NT
40E-10
NT
NT
NT
57E-13
NT
NT
NT
NT
NT
22E 10
19E-11
NT
NT
NT
2 7E-10
NT
58E-10
42E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
92E-11
NT
NT
1 9E-09
NT
1 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
58E-10
NT
NT
NT
BSE-13
NT
NT
NT
NT
NT
33E-10
28E-11
NT
NT
NT
40E-10
NT
85E-10
62E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                           Adult     Child   School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HO       HQ       HQ
62E-08
NT
65E-05
1 6E-05
1 6E-06
2 OE-04
1 OE-08
4 BE -06
1 6E-09
NT
NT
NT
NT
NT
NT
NT
NT
93E-08
IDE -06
29E06
1 5E-07
19E-04
NT
IDE -07
1 5E-08
17E-05
15E^>4
51E-06
NT
9 3E-07
5 4E 07
10E-06
96E-OB
15E-05
NT
47E-08
61E47
NT
NT
6 IE-OS
6 1E-08
61E-07
NT
12E-06
NT
NT
7 3E-07
NT
1 3E 08
5 4E-08
NT
NT
2 3E-07
NT
24E04
6 IE-OS
61E-06
7 4E 04
3 BE -08
18E-05
59E-09
NT
NT
NT
NT
NT
NT
NT
NT
3 5E-07
39E-06
1 1E-05
57E-07
72E-04
NT
3 8E 07
57E08
65E-05
50E-04
19E-05
NT
35E-08
20E-06
3 BE -06
36E-07
56E05
NT
1 7E-07
23E-06
NT
NT
2 3E 07
2 3E-07
23E-06
NT
45E 06
NT
NT
2 7F. 06
NT
50E 08
2 OE 07
NT
NT
1 4E-07
NT
1 5E4)4
37E^»
37E-06
4 5E 04
2 3E-08
1 IE-OS
36E-O9
NT
NT
NT
NT
NT
NT
NT
NT
21E^)7
23E-O6
65E46
35E-07
43E04
NT
23E^)7
35E-08
39E-05
35E-04
12E^)5
NT
21E46
1 2E 06
2 3E-06 -
22EX37
34E-05
NT
1 1E-07
1 4E46
NT
NT
14E-07
1 4E-07
1 4E^6
NT
2 7E-06
NT
NT
1 7E-06
NT
30E 08
t 2E-07
NT
NT
6 2E-08
NT
65E-05
16E-05
16E-06
2 OE-04
1 OE-08
4 BE 06
16E-09
NT
NT
NT
NT
NT
NT
NT
NT
93E4B
10E46
29E06
15E-07
19E-04
NT
t OE-07
1 5E-OB
1 7E 05
t 5E 04
51E-06
NT
9 3E-07
5 4E 07
10E-OB
96E-08
15E-05
NT
47E-08
61E-07
NT
NT
81E08
6 IE 08
6 1E-07
NT
1 2E-06
NT
NT
73E 07
NT
1 3E 08
54E 08
NT
NT
Volume V. Appendix V-14
-------
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                  V   J
TABLE 19  Maximum Inhalation Risks and Noncancer HQs in Subarea SI
CHEMICAL (
CNchlorodMuoromethana
Dichloro«th«n«, 1,1- (Ethylldene dichloride)
Dichloroethene. 1.2-
Dichtoroelhene, 1.1- (VlnyHdine chloride)
Dichtoroethane (trans). 1,2-
Dichlorophenol, 2,4-
Dichtoropropane. 1,2- (Propytene dichloride)
Dtehtoropropene (efs), 1 .3
CHchloropropene (trans), 1.3-
DiethylphftMlat*

Dlmethylphenol, 2.4-
Dimethylphthalate
CN-n-butylphthalata
CNnMrotohMna. 2.6-
tMnttro-2-mafhylphenol, 4,6-
DmMrophenol. 2,4-
DinMiotoluene. 2.4-
Dtoxane. 1.4-
Di(n)octyl phthalate
D. 2.4-
Ethyl methacrylate
Elhy'benzene
Ethytene dlbromida
Ethylene oxlda
Ethylene thtourea
Fluoranthene
Fluor ene
Formaldehyde
Furfural
Heptachlor
Heptachlorobtphenyl
Hexachlorobanzena
Hexachloroblphanyl
Hexachlorobutadlene
Hexachlorocycfohexane, gamma (Llndane)
Hexachtorocydopentadiene
Hexachloroethane ;
Hexachtorophene
Hexanone, 2-
IndenoO ,2.3-cd)pyrene
Isophoron*
Malele hydrazMe
Methoxychlor
Methyl l-buryl ether
Melhyl-2-Pentanona. 4- (MIBK)
Methylene chloride
Methylnaphthalene. 2-
Monochloroblphenyl
Naphthalene
Nrtioanilin*, 2-
Nitroamline. 3-
Inhalatlon
Slope
Factor
mg/kg-d)M
NA
NA
9 1E-02
1 2E+00
NA
NA
NA
13E4M
1 3E-01
NA

NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E»00
NA
7.8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-03
NF .
NA
NA
NA
NF
RAC
(mg?m3)
005
0125
NA
0007875
00175
0002625
0001
0005
0.005
0.7

00175
NA
0.0875
0000875
NF
000175
000175
NA
00175
000875
007875
025
U 00005
NA
000007
0035
0035
0.175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RID
(mg/Vg-d)
HE 02
36E-02
NA
23E-03
50E-03
75E-04
29E-04
14E-03
1 4E-03
20E-01

50E-03
NA
25E-02
25E-04
NF
50E-04
50E-04
NA
50E-03
25E-03
23E-02
71E-02
1 4E-05
NA
20E-05
10E-02
10E-02
50E-02
3 6E-03
1 3E-04
NA
20E-04
NA
50E-05
75E05
50E-06
2 5E 04
7 5E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
57E 03
2 IE 01
NF
NA
10E 02
1 4E 05
NF
Emission
Rate
(g/sec)
25E-04
3E-05
3E-05
3E-05
3E-05
5E-O8
3E-05
3E-OS
3E-05
7E-O5

55E-08
55E-06
16E45
55E-06
55E-06
S5E-06
S5E48
49E-04
55E-06
39E-05
2SE-04
50E-04
1 2E-04
3 IE-OS
15E-10
55E-OB
87E-06
61E-04
55E-06
55E-07
1 4E-08
55E-06
14E-08
1 OE 04
55E-05
55E-06
55E-06
32E-05
64E05
55E06
67E-06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
42E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
51 max
SI max
SI max
51 max
51 max
51 max
SI max
51 max
51 max
SI max
C *J VMAW
o I Trim
SI max
SI max
51 max
51 max
51 max
SI max
SI max
51 max
51 max
51 max
St max
SI max
SI max
SI max
SI max
51 max
51 max
51 max
SI max
SI max
51 max
SI max
SI max
51 max
51 max
51 max
51 max
51 max
St max
51 max
SI max
St max
St ma
51 ma
SI m
SI m
SI m
SI m
Si m
SI m
S1 m
Adult
Cancer
Risk
NT
NT
20E-11
2 7E-10
NT
NT
NT
29E-11
29E-11
NT
NT
n I
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E-09
1 9E-10
NT
NT
NT
49E-10
NT
44E-11
NT
1 6E-10
NT
1 4E-10
NT
NT
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 11
NT
N1
111
NT
NT
Child
Cancer
Risk
NT
NT
51E 11
67E-10
NT
NT
NT
72E-11
72E-11
NT
kJT
n i
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E09
48E-10
NT
NT
NT
12E-09
NT
1 1E-10
NT
40E-10
NT
35E-10
NT
NT
34E-12
NT
NT
NT
NT
NT
NT
NT
tJT
29E 11
NT
NT
NT
NT
NT
School-age
Ca'ncer
Risk
NT
NT
3 IE 11
4 1E-10
NT
NT
NT
44E-11
44E-11
NT

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
24E-09
29E-10
NT
NT
NT
74E-10
NT
67E-11
NT
24E-10
NT
2 1E-10
NT
NT
2 1E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 BE 11
NT
NT
NT
III
NT
Farmer
Cancer
Risk
NT
NT
45E-11
60E-10
NT
NT
NT
65E-11
65E 11
NT
KIT
PI 1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 SE-09
43E-10
NT
NT
NT
1.1E-09
NT
99E-11
NT
35E-10
NT
31E-10
NT
NT
31E-12
NT
NT
NT
NT
NT
NT
NT
NT
2 6E 11
NT
NT
NT
NT
NT
                                                                                                                                           Adult     Child    School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HO       HQ       HQ        HQ
24E06
4 9E-08
NT
7 8E-07
3 5E-07
1 OE 06
6 IE-OB
I2E06
1 2E-06
12E-08
NT
1 5E-07
NT
87E08
3 IE-OS
NT
15E-06
15E-06
NT
15E-07
22E-06
1 5E-08
97E-07
1 tE-03
NT
10E-09
77E-08
93E08
17E06
2 2E 07
8 1E-07
NT
38E-08
NT
2BE4M
I OE-O4
15E04
3 IE 06
60E-05
NT
NT
19E-08
I 3E 07
6 1E-08
8 IE 09
3 IE 07
2 6E 07
NT
NT
7 7E 08
65E 05
NT
90E-06
1 8E-07
NT
29E-06
1 3E-06
36E-06
2 3E 05
46E-06
46E-06
44E-08
NT
57E-07
NT
3 3E-07
1. IE-OS
NT
57E-06
57E-06
NT
5 7E-07
81E06
57E06
36E06
4 2E-03
NT
38E-09
2 9E 07
3 5E-07
83E06
8 OE 07
23E-06
NT
1 4E-05
NT
1 1E-03
38E04
5 7E 04
1 IE 05
2 2E 04
NT
NT
70E 08
48E07
23E 07
30E 08
1 IE 06
9fif 07
NT
NT
296 07
2 -IF 04
NT
54E-06
1 1E-07
NT
1 BE 06
7 9E-07
23E-06
1 4E 05
28E-06
28EOB
2.7E-08
NT
35E-07
NT
20E47
69E-06
NT
35E06
35E-06
NT
35E4)7
49E-06
34E-06
22E06
25E-03
NT
23E-09
1 7E 07
2 1E-07
38E06
49E07
1 4E-06
NT
87E-06
NT
6 4E 04
2 3E 04
35E04
69E06
1 3E-04
NT
NT
42E OB
29E07
1 4E 07
1 BE 08
69E 07
5 BE 07
NT
NT
1 7E07
1 5E-04
NT
24E-06
4 9E-08
NT
7 BE 07
3 5E-07
10E-06
6 IE 06
12E06
12E^W
1 2E-08
NT
15E-07
NT
B7E-08
31E-08
NT
15E^)6
15E-06
NT
1 5E 07
22E46
15E06
9 7E 07
1 1E-03
NT
10E^)9
77EOB
93E-08
1 7E-06
22E4)7
6 1E-07
NT
38E08
NT
2 BE 04
1 OE 04
1 5E-04
3 IE-OB
60E-05
NT
NT
1 9E 08
1 3E 07
6 IE 08
8 IE 09
3 IE 07
26E 07
NT
NT
7 ?E 08
65E 05
NT
Volume V. Appendix V-14
-------
TABLE 19  Maximum Inhalation Hisks and Noneancei HQs in Suh.irea 51
CHEMICAL
Nitroanlline, 4-
Nrtrobenzene
Nitrophenol. 2-
Nibophenot. 4-
N Nitroso-di n-butylamine
N Nitroso-dl n - propylamlne
N-NHrosodlphenylamlne (Diphenylamme)
Nonachkxobiphenyl
Octachlofobiphenyl
Pentachlorobenzene
Pentachtoroblphenyl
Pentachloronitrobenzene
Pentochrorophend
Phenanthrene
Phenol
Pyrana
Safrole (5-(2-Propenyl) 1 .3 benzodioxole)
Styrene
Tebachkxobiphenyt
Tetoachlotoettiine 1,1.1.2
Tetrachloroethane. 1.1.2.2-
Tettachloroefrene
Tetrachkxophenol. 2.3,4,6-
Toluena
rrlchk>ro-1,2,2-trrrtuoroethane. 1 1,2
Frichlorobenzene, 1.2.4
rrtchloroblohefiyt
Trlchloroethan*, 1.1,1- (Methyl chloroform)
frichteroethane, 1.1.2-
frlchloroethene
Irichlorofluofomeltiine
rrlchlorophenol. 2,4.5-
Trlchlorophenol. 2.4.6-
/Inyl acetate
/inyl chloride
(ylene, m/p- (m/p-Dtmethyt benzene)
(ylene. o- (o-Dimethyl benzene)
!.3.7.8-TCDD
I.2.3.7.8-PCDO
1.2.3.4 7.8-HxCDD
'.236.7.8-HxCDO
.2.3 7.8.9 HxCDD
2 3.4 6 7.8 HpCDD
>CDD
'.3.7.8-TCDF
2378PCDF
3 4 7.8 PCDF
.2 3.4 7.8 HxCDF
2 36.7.8-HxCDF
'346 7.8-HxCDF
Inhalation
Slope
Factor
(mg/kg-d)"- 1
NF
NA
NF
NF
54E+OO
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26EX32
20E 01
2 OE-O3
NA
NA
NA
NA
NA
NA
5 7E-02
6 OE-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E*05
75E+04
1 5E+04
1 5E*04
1 5E+04
1 5E«03
1 5E+02
1 5E*04
75E + 03
75E»04
1 5E+04
1 5E»04
1 5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0.002625
002625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
002625
0 1
7 5
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E 04
7 5E-03
NA
1 5E 01
75E-03
NF
7 1E-02
NA
7 5E-03
NA
25E 03
75E 03
2 9E 02
2 1E*00
1 4E-02
NA
7 IE 02
1 OE 03
NA
5 OE 02
2 5E-02
NA
1 4E-02
NA
50E 01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rale
(g/sec)
67E-06
55E-06
6 7E 06
55E 06
1 2E 04
67E06
67E 06
1 4E 08
1 4E-08
48E-05
t 4E-08
34E-05
55E-06
67E-06
55E 06
55E06
1 2E-04
23E-05
1 4E^>8
55E06
55E-06
5 IE 05
6 BE -06
6 IE 04
3 3E-04
55E 06
30E 08
t 3EX»
t 3E 05
19E05
2 5E-04
55E 06
55E-06
64E-05
2 5E-04
3 BE -04
55E-06
108E-11
67BE 11
895E-11
t 66E-IO
1 09E-10
1 24E 09
6 15E 09
B77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
SI max
St max
St max
SI max
St max
SI max
St max
SI max
SI max
SI max
St max
St max
S1 max
St max
SI max
St max
SI max
St max
SI max
St max
St max
SI max
SI max
St max
St max
St max
St max
SI max
SI max
St max
SI max
SI max
St max
SI max
SI max
SI max
St max
SI max
SI max
• SI max
'si max
SI max
SI max
St max
St max
SI max
51 max
SI max
SI max
SI max
Ofl site
Vapor
Cone
(ug/m3)
3 4E 06
2 BE 06
3 4E 06
2 BE 06
6 2E-05
34E 06
3 4E-06
7 1E-O9
7 1E^M
24E-05
7 1E-09
t 7E-05
2 BE 06
34E-O6
28E-06
28E-06
59E05
1 IE-OS
71E-09
2 BE -06
28E06
26E 05
35E-06
3 1E-04
1 7E-04
2 8E-O6
1 5E-08
64E-08
6 4E-06
95E 06
1 2E-04
28E-O6
2 BE -06
33E-05
1 2EX>4
1 9E 04
2 BE -06
55E-12
35E-11
46E 11
84E 11
56E-11
63E-10
3 1E 09
45E 11
1 BE 10
24E 10
7 3E 10
6 BE 10
7 7E-10
Cancer
Adult
Dose
(mg/kg-d)
1 2E-10
99E 11
1 2E 10
99E 11
22E09
1 2E 10
1 2E 10
25E 13
25E 13
BSE 10
25E-13
61E-10
99E 11
1 2E-10
99E-11
99E-11
2 1E-09
40E-10
25E-13
99E-11
99E It
92E 10
1 2E-10
1 1E-08
59E09
99E-11
54E 13
22E 10
22E-10
33E-10
44E-09
99E-11
99E-11
1 2E 09
44E-09
68E-09
99E-11
19E-16
1 2E 15
1 6E 15
30E-15
20E-15
22E-14
1 IE 13
1 6E 15
62E 15
84E 15
26E 14
24E 14
2 7E 14
Cancer
Child
Dose
(mg/kg d)
30E 10
25E-10
30E 10
25E 10
54E 09
30E 10
30E-10
63E 13
63E 13
2 IE 09
63E-13
t 5E 09
25E 10
30E-10
25E-10
25E-10
5 IE 09
1 OE-09
63E-13
25E-10
25E-10
23E-09
30E-10
27E-08
15E-08
25E-10
1 4E 12
56E-10
56E-10
8 3E-tO
1 1E-08
25E-10
25E 10
29E-09
1 IE 08
1 7E 08
25E-10
4 BE 16
30E-15
40E 15
74E 15
49E 15
55E 14
2 7E 13
39E 15
1 5E 14
2 1E 14
6 4E 14
60E 14
6 7E 14
Cancer
School age
Dose
(mg/kg-d)
8E 10
5E 10
BE 10
5E-10
33E 09
8E-10
8E-10
38E-13
38E-13
1 3E 09
36E-13
91E-10
1 5E-10
1 8E-10
1 5E-10
1 5E-10
31E-09
61E-10
3 BE 13
1 5E-10
15E-10
1 4E 09
1 8E-10
17E08
89E-09
1 5E-10
82E 13
34E-10
34E-10
50E-10
66E-09
5E-10
5E-10
7E-09
66E-09
OE-08
5E-10
29E-16
18E 15
24E 15
45E 15
29E 15
34E 14
1 7E 13
2 4E 15
93E 15
1 3E 14
39E 14
36E 14
4 1F 14
Cancer
Farmer
Dose
(mg/kg d)
2 7E 10
2 2E 10
2 7E 10
22E 10
4 BE 09
2 7E-10
2 7E 10
56E-13
56E 13
1 9E 09
56E 13
1 3E 09
22E-10
27E-10
22E 10
22E-10
46E 09
90E-10
56E 13
22E 10
22E-10
20E09
2 7E-10
2 4E 08
1 3E 08
22E-10
t 2E 12
50E 10
506-10
74E 10
98E-09
22E-10
22E-10
26EO9
9 BE -09
1 5E-08
22E-10
43E 16
27E-15
36E-15
66E-15
43E 15
49E 14
25E 13
35E 15
1 4E 14
1 9E 14
5 7E 14
5 3E 14
6 OF 14
Noncancer
Adult
Dose
(mg/kg d)
93E 10
77E 10
93E-10
77E 10
17E08
93E 10
93E 10
20E 12
20E 12
66E 09
20E 12
47E09
77E-10
93E-10
77E 10
77E-10
t 6E-08
3 IE 09
20E-12
7 7E-10
77E-10
72E-09
95E 10
86E08
46E08
77E-10
42E-12
1 7E 09
17E09
26E09
34E08
77E-10
77E-10
90E09
3 4E 08
5 3E 08
77E 10
15E 15
95E 15
t 2E 14
23E-14
1 5E-14
1 7E 13
86E 13
1 2E 14
4 BE 14
65E 14
20E 13
1 9E 13
2 IF 13
Noncancer
Child
Dose
(mg/kg d)
35E 09
29E09
35E09
29E09
63E 08
35E-09
35E 09
73E-12
73E 12
25E-08
73E 12
1BE08
29E4J9
35E-09
29E-09
29E-09
6 OE-08
1 2E-08
73E 12
29E-O9
29E09
2 7E-08
35E-09
3 2E-07
17E-07
29E49
1 6E-11
65E09
65E-09
97E-09
1 3E 07
29E09
2 9E-O9
34EC8
1 3E 07
2 OE 07
29E-09
56E 15
35E 14
47E 14
86E 14
5 7E 14
65E 13
32E 12
4GE 14
1 BE 13
2 4E 13
74E 13
70E 13
79F 13
Moncancer
School-age
Dose
(mg/kg-d)
2 IE 09
1 7E 09
2 IE 09
1 7E 09
3 BE 08
2 IE 09
21E09
44E 12
44E 12
1 5E 08
44E 12
1 IE 08
1 7E-09
2 IE 09
1 7E-09
1 7E 09
36E-08
7 IE 09
44E 12
17E09
1 7E-09
16EOB
2 1E-O9
1 9E 07
10E07
1 7E 09
95E 12
39E 09
39E 09
59E09
7 7E 08
1 7E 09
t 7E 09
20E 08
7 7E 08
1 2E 07
1 7E 09
34E 15
2 IE 14
2 BE 14
52E 14
34E 14
39E 13
1 9E 12
2 BE 14
1 IE 13
1 5E 13
45E 13
42E 13
4 7E 13
Noncancer
Farmer
Dose
(mo/kg d)
93E-10
77E 10
93E 10
77E 10
1 7E 08
93E 10
93E 10
20E 12
20E 12
66E09
20E 12
47E«9
77E 10
93E-10
77E 10
77E-10
1 6E-08
3 1E-O9
20E-12
7 7E 10
77E 10
72E09
95E 10
86E-08
4 BE 08
77E-10
42E-12
1 7E4>9
1 7E-09
26E09
3 4E-08
77E 10
77E 10
9 OE-09
34E-08
5 3E-08
77E-10
1 5E 15
95E 15
t 2E 14
23E 14
15E 14
1 7E 13
86E 13
1 2E 14
48E H
65E 14
20E 13
1 9E 13
? IF 11
 olume V, Appendix V-14
-------
TABLE 19  MaximumV
                      A\on Risks and Noncancer HQs in Subarea S1
CHEMICAL
NHioaniHne, 4-
NHrobenzene
NHrophenol, 2-
Nrtrophenol. 4-
N-Nitroso-dl-n-butylamine
N-NHroso-dl-n-propylamine
N-NHrosodlphenytamlne (Diphenylamlne)
Nonachlorobiphenyl
OctachtoroWphenyi
Pentachhxobenzene
Pentachkwoblphenyl
PentachfofonHrobenzene
Penbachkwophenol
Ftienarrthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl)-1 .3-benzodloxole)
Styrene
Tetrachloroblphenyl
Tetrachloro«thane. 1.1.1.2-
Tebachloroelhane. 1.1.2.2-
Tetrachloroethene
Tetrachfcxophenol, 2.3.4.6-
Toluene
Trichloro-1.2.2-trifluofoethane, 1.1.2-
Trichlorob*nz«ne. 1,3,4-
Trtchteroblphonyl
Trtchkxoethane. 1,1,1- (Methyl chloroform)
TrtcMoroethane, 1.1.2-
Trichtoroethene
Trlchlorofluoromethane
Trichlorophenol. 2.4.5-
Trlchlorophenol. 2,4,6-
Vinyl acetate
Vinyl chloride
Xylene, m/p- (m/p-Dlmethyl benzene)
Xylene, o- (o-Ofmethyl benzene)
2.3.7.8-TCDO
1.2.3,7,8-PCDD
1.2.3.4.7,8-HxCDD
1.2.3.6.7.6-HxCDO
1.2.3,7.8,9-HxCDO
1.2,3,4,6.7.8-HpCDD
OCDD
2.3.7.8-TCDF
1,2,3.7.8-PCDF
2.3.4.7.8-PCDF
1.2.3.4.7.8-HxCDF
1,2.3,6,7.8-HxCDF
2.3.4.6.7.8-HxCDF
Inhalation
Slope
Factor
(mg/kg-d)*-1
NF
NA
NF
NF
54E*00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E-02
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
10E-02
NA
30E-01
NA
NA
15E*05
7 5E+04
1 5E+04
1 5E+04
1 5E+04
1 5E+03
1 5E»02
1 5E+04
7 5E+03
7 5E*04
1 5E«04
1 5E*04
1 5E+04
RAG
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
002625
NF
025
NA
002625
NA
000675
002625
01
75
005
NA
025
00035
NA
0.175
00875
NA
0.05
NA
1.75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
15E-01
75E-03
NF
7 1E-02
NA
75E-03
NA
25E-03
75E-03
29E-02
2 1E»00
1 4E-02
NA
71E-02
10E-03
NA
50E-02
25E-02
NA
1 4E-02
NA
50E-01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rale
(g/s«c)
67E-06
55E-06
67E-06
55E-06
1 2E-04
67E-06
67E-06
1 4E-08
14E-08
4 BE -05
1 4E-08
34E-05
55E-08
87E-06
55E-06
55E-06
1 2E-04
23E-05
1 4E-08
55E-06
55E-06
5 IE-OS
66E46
6 IE 04
33E-04
55E-06
30E-08
13E-05
1 3E-05
19E-05
25E-04
55E-06
55E-06
64E-05
2 5E-04
3 BE -04
55E-06
1 OBE-11
678E-11
B95E-11
1 66E 10
109E 10
1 24E 09
6 15E-09
877E 11
345E 10
467E-10
1 43E-09
1 33E 09
1 50E 09
Subarea
SI max
St max
51 max
SI max
SI max
51 max
SI max
SI max
St max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
S1 max
51 max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
SI max
St max
SI max
SI max
SI max
SI max
SI max
SI max
51 max
SI max
SI max
SI max
SI max
St max
51 max
5) max
SI max
SI max
SI max
SI max
SI max
51 max
Adult
Cancer
Risk
NT
NT
NT
NT
1 2E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E-12
20E-11
19E-12
NT
NT
NT
NT
NT
NT
13E-11
20E-12
NT
NT
99E-13
NT
13E-09
NT
NT
29E-11
9 1E-11
24E-11
4SE-11
29E-11
33E 11
1 7E-I1
24E-11
46E-11
63E 10
3 BE 10
36E 10
4 1E-10
Child
Cancer
Risk
NT
NT
NT
NT
2 9E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E-12
50E-11
4 7E-12
NT
NT
NT
NT
NT
NT
32E-11
50E-12
NT
NT
25E-12
NT
3.3E-09
NT
NT
72E-11
23E-10
60E-11
1 1E-10
73E 11
83E 11
4 IE-II
59E 11
1 2E 10
1 6E 09
96E 10
90E 10
1 OE 09
School-age
Cancer
Risk
NT
NT
NT
NT
1 BE -08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E 12
30E-11
2 8E-12
NT
NT
NT
NT
NT
NT
19E-11
30E-12
NT
NT
1 5E-12
NT
20E-09
NT
NT
44E-11
1 4E-10
36E-11
67E-11
44E 11
50E 11
25E 11
36E 11
70E 11
95E 10
5 BE 10
54E 10
6 IE 10
Farmer
Cancer
Risk
NT
NT
NT
NT
2 BE -08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
57E-12
45E-11
42E-12
NT
NT
NT
NT
NT
NT
28E-11
44E-12
NT
NT
22E-12
NT
29E-09
NT
NT
65E-11
2 OE-10
54E-11
99E-11
65E 11
74E 11
37E II
52E 11
1 OE 10
1 4E 09
BSE 10
BOE 10
90E 10
                                                                                                                                         Adult      Child    School-age  Farmer
                                                                                                                                       Noncancer Noncancer Noncancer Noncancer
                                                                                                                                          HQ       HQ       HQ       HQ
NT
54E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
63E-06
10E-07
NT
51E-09
10E-07
NT
44E-08
NT
10E-07
NT
29E06
1 3E 07
30E-06
22E-08
54E-08
NT
24E-08
1 7E-06
NT
6 BE -07
31E-08
NT
BSE -07
NT
1 IE 07
15E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
ru
NT
IK
Ml
NT
20E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
23E45
3.8E-07
NT
19E-08
3 BE -07
NT
16E-07
NT
3 BE -07
NT
1 IE-OS
47EXJ7
11E45
80E-06
20E-07
NT
91E48
65E-06
NT
26E-06
1 1E-07
NT
23E08
NT
40E-07
57E09
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
NT
HT
NT
NT
1 2E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
14E-05
2 3E-07
NT
12E08
23E-07
NT
99E-08
NT
2.3E-07
NT
6SE-06
29E-07
6 BE 46
49E-08
1 2E-07
NT
S5E08
39E-06
NT
15E-06
69E-OB
NT
1 4E-06
NT
24E07
35E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
IIT
NT
NT
54E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
63E46
10E-07
NT
5 IE 09
10E-07
NT
44E-08
NT
10E^)7
NT
29E-06
13E-07
30E08
22E08
S4E-OB
Ni
24E-08
1 7E-06
NT
6 BE 07
31E-08
NT
8 3E-07
NT
1 IE 07
15E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
W
Volume V. Appendix V-14
-------
TABLE  19  Maximum Inhalation Risks and Noncancel HQs in Subaiea S1
CHEMICAL
1.2.3,7,B.9-HxCDF
1. 2.3.4.6.7,8 HpCDF
l.2.3,4.7.8,9-HpCDF
OCDF
Dioxln TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
^articulate mattei
3aspirable participates
Inhalation
Slope
Factor
(mg/kg-d)"-!
1 5E»04
1 5E«03
1 5E»03
1 5E*02

NA
MA
SO
NA
84
61
41
NA
NA
NA
NA
004
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0 004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE4M
75E-05
36E05
1 3E 03
1 3E 04
1 3E 03
2 5E-01
NA
NA
2 1E OS
50E 03
1 3E^)3
1 3E 03
t BE 05
75E 02
50E 04
NA
NA
NA
NF
Emission
Rale
(g/sec)
293E-10
930E-09
1 22E-09
1 89E-08
4 2BE-08
24E-04
42E-06
37E-05
1 5E-04
33E-08
16E4)5
7 1E-07
71E-07
94E^>5
43E4»
1 4E^)3
50E-06
4 7E^>4
1 5E45
34E4»
1 2E-04
32E-02
24E«00
91E^>2
72E42
72E^32
Subarea
SI max
SI max
St max
SI max

SI max
S1 max
SI max
SI max
SI max
St max
SI max
SI max
SI max
S1 max
SI max
SI max
SI max
51 max
SI max
SI max
SI max
SI max
SI max
S1 max
S1 max
Off sits
Vapor
Cone
(ug/m3)
1 5E-10
4 7E 09
62E 10
9 7E-09

1 2E-04
21E-06
19E-05
77E-05
1 7E-08
82E-06
3 6E-07
36E 07
4 BE 05
22E 05
7 1E-04
26E-06
2 4E-04
7 7E 06
1 7E 05
6 1EX»
1 6E-02
1 2E«00
46E^>2
3 7E 02
3 7E-02
Cancer
Adult
Dose
(mg/kg d)
53E 15
1 7E 13
2 2E 14
34E 13
77E-13
4 3E 09
75E 11
66E-1Q
27E-09
59E-13
29E-10
1 3E-11
1 3E-11
1 7E-09
77E 10
2 5E 08
90E-11
84E 09
2 7E-10
6 IE 10
22E-09
5 7E-07
4 3E-05
1 BE 06
1 3E 06
1 3E 06
Cancer
Child
Dose
(mg/kg-d)
1 3E-14
42E 13
55E 14
85E-13
1 9E 12
1 IE 06
1 9E-10
1 7E-09
67E-09
15E-12
72E-10
32E-11
32E-11
42E 09
19E-09
63E-08
22E-10
2 1E-08
67E-10
1 5E 09
54E-09
1 4EO6
1 1E44
4 1E-06
32E4W
32E-06
Cancer
School-age
Dose
(mg/kgd)
79E-15
25E-13
33E-14
51E-13
1 2E 12
65E09
1 1E-10
1 OE 09
4 1E-09
89E 13
43E-10
1 9E-11
1 9E-11
25E-09
1 2E 09
3 8E 08
1 4E-10
1 3E-08
41E 10
92E 10
32E-09
8 7E-07
65E-05
25E-06
19E06
1 9E-06
Cancel
Faimei
Dose
(mg/kg-d)
1 2E 14
37E 13
49E-14
76E 13
1 7E-12
96E09
1 7E 10
15E09
60E-09
1 3E-12
84E-10
28E 11
28E-11
36E-09
1 7E-09
56E-08
20E-10
19EX)8
60E-10
1 4E 09
4 BE -09
1 3E-06
97E^)5
36E-06
29E-06
29E-06
Noncancer
Adult
Dose
(mg/kg d|
4 IE 14
1 3E 12
1 7E-13
26E 12
60E-12
34E4)8
59E-10
5 2E-09
2 IE 08
46E-12
22E-09
99E-11
99E 11
1 3E 08
60E-09
20E^)7
70E 10
66E438
2 1E 09
47E^)9
1 7E-08
45E«
34E44
1 3E 05
10E05
1 OE-05
Noncancel
Child
Dose
(mg/kg-d)
1 5E 13
49E 12
64E-13
99E 12
22E 11
1 3E 07
22E09
19E08
7 BE -08
1 7E-11
84E-09
3 7E-10
37E-10
4 9E-08
22E-08
73E-07
26E09
25E^)7
7 BE 09
1 8E 08
63E-OB
17E05
1 3E 03
47E05
38E05
3 BE 05
Noncancel
School-age
Dose
(mg/kg-d)
92E-14
29E 12
39E-I3
60E 12
1 3E-11
76E 08
1 3E 09
1 2E 08
4 7E 08
10E-11
50E09
22E 10
22E 10
30E 08
1 4E 08
44E07
16E09
15E^7
47E09
1 1E-08
3 BE -08
1 OE 05
76E04
29E 05
23E05
2 3E 05
Noncancer
Farmer
Dose
(mg/kgd)
4 1E-14
1 3E 12
1 7E-13
26E-12
60E-12
34E48
59E-10
52E09
2 IE 08
46E 12
22E4»
99E-11
99E 11
1 3E 08
60E09
20E07
70E 10
66E 08
2 1EO9
4 7E 09
1 7E-08
45E06
34E04
13E05
1 OE 05
1 OE 05
  NA - Not applicable
  NF • Not found
  NT * No toxlclty Information
  HO * Hazard quotient
  HI - Hazard Index
 olume V, Appendix V-14
-------
TABLE 19  Maximum Iv    .ion Risks and Noncancet HQs in Subaiea S1



CHEMICAL
1.2.3,7,8.9-HxCDF
1,2,3.4.6,7,8-HpCDF
1.2.3.4,7.8.9-HpCDF
OCDF
CNoxin TEQ
Aluminum
Antimony
Arsenic
Barium
BeryflHim
Cadmium
Chromium (haxavalent)
Chromium (bivalent)
Copper
Lead
Mefcury (and MeHg)
Nickel
Selenium
Silver
ThalHum
Zinc
Hydrogen chloride
Total nitrogen oxide* (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Resplrable paniculate*
Inhalation
Slope
Factor
(mg/Kg-d)A-1
1 5E+04
1 5E»03
1 5E*03
1 5E+02

NA
NA
50
NA
84
6.1
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF


RAC
(mgfmS)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF

Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
IDE -04
75E-05
386-05
13E-03
1 3E-04
13E-03
25E-01
NA
NA
2 IE-OS
50E-03
1 3E-03
1 3E 03
1 6E-05
75E-02
50E-04
NA
NA
NA
NF

Emission
Rate
(Jl/sec)
2 93E-10
930E-09
1 22E-09
189E-08
428E-08
24E-04
42E4M
37E-05
15E-04
33E-O8
16E-05
71E-07
71E-07
94E-05
43E-05
14E-03
SOE^W
47E-04
15E-05
34E-05
12E-04
32E-02
24E+00
91E-O2
72E^>2
7.2E-02



Subarea
SI max
S1 max
SI max
SI max

SI max
SI max
SI max
SI max
SI max
SI max
SI max
S1 max
SI max
SI max
SI max
SI max
SI max
51 max
SI max
SI max
SI max
SI max
S1 max
SI max
S1 max

Adult
Cancer
Risk
79E-11
25E-10
33E-11
5 IE 11
25E-09
NT
NT
33E-08
NT
50E-12
18E-09
52E-10
NT
NT
NT
NT
75E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT

Child
Cancer
Risk
20E-10
62E-10
82E-11
13E-10
63E-09
NT
NT
83E-08
NT
12E-11
44E-09
1 3E-09
NT
NT
NT
NT
19E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT

School-age
Cancer
Risk
1 2E-10
3 BE 10
50E-11
77E-11
38E09
NT
NT
50E-08
NT
7 5E-12
26E-09
79E-10
NT
NT
NT
NT
1.1E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT

Farmer
Cancer
Risk
1 8E-10
56E-10
73E-11
1 IE 10
56E-09
NT
NT
74E-08
NT
1 IE 11
39E09
12E-09
NT
NT
NT
NT
1 7E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NOTES:
  NA-Not applicable
  NF-Not found      ^
  NT « No toidcfty Information
  HQ - Hazard quotient
  HI -HazardIndex
                                                                             Total Risk   56E-08   14E-07    84E-08    1.2E-07
                                                                                                                                          Adult     Child   School-age  Farmer
                                                                                                                                        Noncancer Noncancer Noncancer Noncancer
                                                                                                                                           HQ       HQ       HQ       HQ
NT
NT
NT
NT
NT
NT
59E48
69E-05
59E-04
37E-09
16E-05
79E-08
40E-10
NT
NT
91E-03
1 4E-07
53E-05
17E-06
2 7E 04
22E-07
89E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E-05
26E-04
22E-03
1 4E-08
67E-05
30E-07
15E-O9
NT
NT
34E-02
52E-07
20E-04
63EXM
IDE -03
84E47
33E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
13E-05
1 6E-04
1 3E-03
B3E-09
40E05
1.8E-07
90E-10
NT
NT
21E-02
3 2E 07
12E04
38E06
6 1E-04
50E-07
20E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
59E46
69E-05
59E-04
37E-09
18E-05
79E08
40E-10
NT
NT
9 IE 03
1 4E 07
53E-05
17E06
27E-04
22E-07
B9E-O3
NT
NT
NT
NT
                                                                                                                                Total HI   22E-02   81E-02    49E-02    2 2E-02
Volume V, Appendix V-14
-------
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-------
TABLE 20  Maximum
                       , ion Risks and Noncancer HQs in Subarea S2
CHEMICAL
Acenaphthene
Acenaphthytone
Acetaldehyde
Acetone
Acetophenone
Acrytonltrlle
Anthracene
Benzene
Benzole acid
BenzoWchkxIde
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)fluoranthene
Bento(g,h.l)p«fy»ene
B«nzo(k)fluoranlhene
Bls(2-chloroethoxy) methane
Bls(2-chtoroethyl)ether
Bls(2-chlorc4sopropyT)elher
3l»(2-ethylhexy1)phthBl8te
Bromodlchloromethane
Bromoform
Sromomethane
Bromodlphenyl ether, p-
Sutanone, 2- (Methyl ethyl ketone)
Sutylbenzylphthalate
laibon dlsurfide
Carbon tetrachlortde
^hlordane
;hk>ro-3-methylphenol, 4-
:hkjroanlline. p- (4-Chlofoinlllne)
:hk>robenzene
;hlorobenzllate
;hloroethane (Ethyl chloride)
Chloroform
;hloromethane
:hloronaphthalene. bet*
;hlorophenol, 2-
;hlorodiphenyl ether. 4- v
;hrysene
'resol, m-
Iresol. o- (2-Methylpnenol)
:t«sol. p-
;rotonaldehyde
;umene
)DE, 4.41-
)ibenz(a.h)anthracene
Nbromochloromethane
)ichlorobenzene. 1 ,3-
>ichlorobenzene, 1 .4-
Mchlorobenzene, 1 .2-
lichloroberuidine, 3.3'-
>ichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg-d)A-1
MA
NF
77E-03
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
13E+00
NF
NA
NA
27E-01
NA
81E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA •
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00675
00875
00005
02S25
00015
3.5
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0005
00175
2.5
000875
NA
007
0 004375
NF
NA
0 04375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E-04
2 5E-02
2 5E 02
1 4E-04
75E^)2
43E-O4
lOEtOO
NA
NA
NA
NA
NA
NA
NA
NA
lOE^H
50E-03
50E4>3
50E-03
36E-04
NA
7 IE 02
50E02
7 1E-04
1 4E44
1 5E-05
NF
1 OE-03
1 4E-03
5 OE-03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E-02
1 3E-02
1 3E-03
NA
64E-04
NA
NA
5 OE-03
NA
57E 02
1 4E 02
NA
NA
Emission
Rale
(g'sec)
67E-06
67E-08
30E-04
2 9E-03
2 9E-04
20E-04
55E08
15E-05
1 IE-OS
32E-05
55E08
55E08
55E-08
55E-08
S5E-08
67E-06
1 3E-05
67E-08
37E-05
10E-04
S5E-08
49E-04
67E-06
5 IE-OS
55E08
89E-05
16E-04
55E-07
67E06
67E-08
55E06
37E-05
4 9E-04
2 7E-04
2 5E 04
67E06
55E 06
67E06
55E 06
55E06
55E06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
SZmax
S2 max
S2ma«
S2 max
S2 max
S2max
S2 max
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
52 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
52 max
S2 max
S2 max
S2 max
S2 max
S2 max
52 max
S2 max
S2 max
52 ma>
52 man
52 ma.
S2 max
52 max
S2 max
52 max
Adult
Cancer
Risk
NT
NT
1 1E-11
NT
NT
24E-10
NT
21E-12
NT
NT
NT
NT
NT
NT
NT
NT
72E-11
NT
NT
NT
1 OE-13
NT
NT
NT
NT
NT
41E-11
35E-12
NT
NT
NT
50E-11
NT
1 1E-10
76E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
28E-11
NT
NT
59E-10
NT
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 8E-10
NT
NT
NT
26E-13
NT
NT
NT
NT
NT
10E-10
87E-12
NT
NT
NT
1 2E-10
NT
26E-10
1 9E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HI
NT
NT
NT
School-age
Cancer
Risk
NT
NT
1 7E-11
NT
NT
36E-10
NT
32E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
1 6E-13
NT
NT
NT
NT
NT
62E-11
53E-12
NT
NT
NT
75E-11
NT
1 6E-10
1 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
2 5E-1 1
NT
NT
5 3E-10
NT
4 7E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
23E-13
NT
NT
NT
NT
NT
9 IE 11
78E-12
NT
NT
NT
1.1E-10
NT
2 3E-10
17E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                         AduK      Child   School-age  Farmer
                                                                                                                                       Noncancer Noncancer Noncancer Noncancer
                                                                                                                                          HQ       HQ       HQ       HQ
1 7E-08
NT
1 8E-05
44E-06
45E-07
54E-05
2 BE -09
13E06
4 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
26E-08
2 9E-07
79E-07
42E-08
53E-05
NT
2 BE -08
42E-09
48E-06
42E-C5
1 4E-08
NT
2 6E-07
1 5E 07
2 BE -07
26E-08
4 IE-OS
NT
1 3E-OB
1 7E-07
NT
NT
17E^)8
1 7E-08
1 7E-07
NT
33E-07
NT
NT
20E07
NT
3 7E 09
t 5E 08
NT
NT
6 4E-08
NT
67E05
1 7E-05
1 7E-06
20E-04
1 IE 08
49E06
16E-09
NT
NT
NT
NT
NT
NT
NT
NT
96E-08
1 IE-OS
30E-08
16E-07
20E-04
NT
10E-07
16E-08
1BE-05
16E-04
S3E-O6
NT
96E07
55E-07
1 IE 08
9 BE -08
1.5E-05
NT
4 BE 08
63E-07
NT
NT
6 3E 08
6 3E 08
63E07
NT
1 2E 06
NT
NT
75E 07
NT
1 4E 08
5 5F 08
NT
NT
39E-08
NT
4 IE-OS
10E-05
IDE 06
1 2E-04
63E-09
30E-06
9BE-10
NT
NT
NT
NT
NT
NT
NT
NT
58E-08
64E-07
1BE-08
9SE-OS
12E-04
NT
62E08
95E-09
1 IE-OS
96E-05
32E06
NT
58E07
33E07
B4E07
S 9E-08
92E-08
NT
29E-08
3 BE -07
NT
NT
3 BE 06
3 BE 08
3 BE 07
NT
74E 07
NT
NT
46E 07
NT
83E 09
3 IF. .08
NT
NT
1 7E-08
NT
18E05
44E-06
4 5E-07
54E-05
28E-09
1 3E-06
43E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 BE 4)8
29E47
79E-07
42E48
53E4B
NT
2 BE 08
42EXI9
48EC6
42E05
1 4E-06
NT
2 6E-07
1 5E4>7
2 BE 07
2 6E 08
4 IE 06
NT
1 3E-OB
1 7E-07
NT
NT
1 7E 08
t 7E 08
1 7E-07
NT
33E07
NT
NT
2 OE 07
NT
37E 09
1 5E 08
NT
NT
  olumeV. Appendix V-14
-------
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-------
TABLE 20  Maximum Inhalation Risks and Noncancet HQs In Subarea 52



CHEMICAL
Dichlorodifluoromethane
Dichloroethane, 1,1- (Ethyliden* dlchloride)
Dichloroathane. 1,2-
Dichloroelhene. 1,1- (Vlnylidlne chloride)
DtchkxoathMie (trans). 1.2-
Dichlorophenol, 2,4-
Dichloropropana, 1 ,2- (Pr. • <»n« dichtotld*)
Dlchloropropene (els), 1 ..1
Dtchtoropropene (trans), 1 ,3-
Dlethyiphthatola
tNmethoxybenzldln*. 3,3'-
Dimethytphanol, 2,4-
Dimalhylphthaiate
Dt-n-butytphthalat*
DinKrotoruene. 2,6-
Dinrbo-2-memylphenol, 4.6-
DinHrophenol, 2.4-
DinHrotohjen*. 2,4-
Dloxana. 1,4-
Oi(n)odylphthafale
0,2.4-
Ethyl methacrytate
Ettiy">anzene
Ethytene dfbromlda
Ethylene oxide
Etttyienemtourea
Fruoranthene
Fluorerw
Formaldehyde
Furfural
Heptachlof
Htfptechlofobfpnenyl
Hexachlorobeniene
Hexachloroblphenyl
Hexachlorobutadien*
Haxachtorocyclohexane. gamma (Undana)
Hexachtorocyclopentadien*
Hexachtofoelhane '
Haxachlorophene
Haxanona, 2-
lndeno( 1 .2 ,3-cd)pyTene
rsophorone>
Malaic hydrazlda
Methoxycblor
Methyl 1 butyl ether
Merhyl-2-Pentanone. 4- (MIBK)
Melhylene chlorida
Methytnaptithalana, 2-
Monochlorobiphenyl
Naphthalene
Nrtioaniline. 2-
Nitroaniline, 3-
Inhalation
Stop*
Factor
8
58E-08
1 IE 08
1 3E-07
3 BE -07
NT
24E-06
NT
1 7E-04
6 3E-05
95E 05
19E-06
37E-05
NT
NT
1 2E 08
80E08
38E 08
5 IE 09
1 9E 07
1 6E-07
NT
NT
48E 08
4 1E 05
NT
6 6E 07
1 3E-08
NT
2 1E-07
9 6E-08
2 BE 07
1 7E-06
3 4E 07
3 4E 07
32E-09
NT
42E-08
NT
24E-08
84E-07
NT
42E47
42E-07
NT
42EXW
60E-07
42EXJ7
27E4)7
31E-04
NT
28E-10
21E-08
26E-08
47Efl7
59E08
17E07
NT
1 1E-08
NT
77E^)5
2 BE 05
42E05
84E07
16E-05
NT
NT
5 IE 09
35E08
1 7E 08
22E09
8 IE 08
7 IE 08
NT
NT
2 1E08
1 8E 05
HI
Volume V, Appendix V-14
-------
TABLE 20 Maximum Inhalation Risks and Uoncancei HQs in Subaiea S2
CHEMICAL
Niboanllina, 4-
Nitrobenzene
Nibophenol. 2-
Nibophenot, 4-
N Nrboao-di-n-butylamine
N-Nitroso-dl-n-propylamrne
N-NHrosodlphenylamlne (Diphenylamine)
Nonachloroblphenyl
Octachlofobiphenyi
Pentachlorobenzene
Pentachlorobiphenyf
Pentachloronrboberusne
Pent»chk>rophenol
Phenanthrene
Phenol
Pyrsn*
Safrole (S-(2-Prop*nyO-1 .3 benzodioxole)
Styrene
Tebachloroblphenyl
febachloioethane. 1.1.1.2-
(etaachloroemane. 1, 1.2.2-
T eb achlor oethene
lebachlorophenol. 2.3,4 6-
Toluene
rrlchloro-1,2.2-bifluoroethane. 1.1 2-
frlchlorobenzene. 1.2,4-
T rlchlof oblphenyl
[nchloroethane. 1,1.1- (Methyl chloroform)
rrichloroethane. 1.1,2-
frlchloroettiene
rrkhlorofluoromethane
rrichlorophenot. 2.4.5-
rkhlorophenol. 2,4,6-
/inyl acetate
'inyl chloride
Cylene. m/p- (m/p-Dimethyl benzene)
[ylene, 0- (o-Dimettiyt benzene)
,3,7,8-TCDD :
,2.3.7.B-PCDO
.2.3 4.7.8 HxCDO
,2.367.8-HxCDD
2 3 7.8.9 HxCDO
.2,3.4.6, 7,8-HpCDD
)CDO
.3.7.8TCDF
2.3,7,8PCDF
34 7.8PCDF
2 34 7,8 HxCDF
2 3 6, 7.8 HxCDF
3 4 6 7,8 HxCDF
}lume V, Appendix V 14
i r\
Inhalation
Slope
Factor
(mg/kg-d)*- 1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E 02
20E-01
2 OE-03
NA
NA
NA
NA
NA
NA
5 7E 02
6 OE-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
15E+05
75E + 04
5E»04
5E»04
5E+04
5E»03
5E»02
1 5E*04
75E*03
75E«04
1 5E*04
1 5E«04
1 5E«04


RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
MA
NA
NA
NA
0002625
002625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
Q 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA


Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
7 5E-03
NA
1 5E-01
75E-03
NF
7 1E-02
NA
7 5E-03
NA
25E03
75E 03
29E 02
2 1E»00
1 4E-02
NA
7 IE 02
1 OE 03
NA
50E 02
25E-02
NA
1 4E-02
NA
50E 01
50E 01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA


Emission
Rale
(g/sec)
6 7E^)6
55E 06
67E 06
55E4J6
1 2E 04
67E 06
67E 06
1 4E-06
1 4E-08
4 BE 05
1 4E-08
34E45
S5E-06
67E-06
55E-06
55E06
1 2E 04
23EO5
1 4E 08
55E-06
55EXW
5 1E45
68E06
6 IE 04
33E 04
55E 06
30E-08
1 3E-05
1 3E-05
1 9E-05
25E04
55E06
55E-06
6 4E-05
25E-04
3 BE 04
55E06
1 08E-11
6 78E-11
895E 11
166E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09


Subarea
S2 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
S2 max
52 max
52 max
52 max
S2 max
52 max
52 max
52 max
S2max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
S2 max
52 max
S2 max
52 max
52 max
52 max
52 max


Off site
Vapor
Cone
(ug/m3)
94E-07
7 7E 07
94E 07
7 7E^)7
1 7E-05
94E 07
94E07
20E-09
20E-09
67E-06
20E-09
47E-06
7 7E-07
9 4E-07
77E-07
7 7E-07
1 6EO5
32E-06
20E-09
7 7E 07
7 7E-07
72E-06
95E 07
86E-05
46E 05
77E 07
42E09
1 BE 06
1 BE -06
26E 06
34E-05
7 7E 07
7 7E-07
90E-06
34E05
53E-05
7 7E-07
1 5E 12
95E 12
1 3E 11
23E 11
t 5E 11
1 7E 10
B6E 10
1 2E-11
4 BE 11
65E 11
20E 10
1 9E 10
2 1E-10


Cancer
Adutt
Dose
(mg/kg-d)
33E 11
2 7E-11
33E 11
2 7E 11
60E-10
33E 11
33E-11
69E 14
69E-14
23E 10
69E-14
1 7E 10
27E 11
33E-11
27E-11
2 7E 11
5 7E 10
1 IE 10
69E-14
27E-11
2 7E-11
25E-10
34E-11
30E-09
1 6E-09
27E-11
1 5E-13
62E-11
62E-11
92E 11
1 2E-09
27E-11
27E-11
32E-10
12E-09
1 9E 09
27E-11
53E-17
33E 16
44E 16
82E 16
54E 16
6 IE 15
30E 14
43E 16
1 7E 15
23E 15
70E 15
66E 15
74E 15

^
Cancer
Child
Dose
(mg/kg d)
82E-11
68E-11
82E 11
68E-11
1 5EO9
82E-11
82E 11
1 7E-13
1 7E 13
5 BE 10
1 7E-13
4 1E-10
6 BE 11
82E-11
68E-11
68E-11
1 4E 09
2 BE 10
1 7E-13
6 BE 11
68E-11
63E-IO
84E-11
75E09
4 1E-09
68E-11
37E 13
1 5E-10
1 5E 10
23E-10
30E-09
6 BE 11
68E-11
79E-10
30E-09
47E-09
68E-11
1 3E-16
83E 16
1 IE-IS
20E 15
1 3E 15
1 5E 14
7 5E 14
1 IE 15
42E 15
5 7E 15
t BE 14
1 61 14
1 BE 14


Cancer
School-age
Dose
(mg/kgd)
50E 11
4 1E-11
50E-11
4 1E-11
90E-10
50E-11
50E-11
1 OE-13
1 OE-13
35E-10
1 OE-13
25E-10
41E-11
50E-11
41E-11
41E-11
85E 10
1 7E 10
1 OE-13
4 IE 11
4 IE 11
3 BE 10
50E-11
45E09
24E-09
4 IE 11
22E 13
93E-11
93E 11
1 4E-10
1 8E-09
4 IE-It
4 IE-It
48E-10
18E-09
2 BE 09
4 IE-It
80E 17
50E 16
66E 16
1 2E 15
8 1E 16
92E 15
46E 14
65E 16
26E 15
35E 15
1 1E 14
99E 15
t IE 14


Cancer
Farmer
Dose
(mg/kg d)
73E-11
60E 11
73E 11
60E 11
13E09
73E-11
73E-11
1 5E-13
15E-13
52E-10
15E-13
37E 10
60E 11
73E-11
60E 11
60E 11
1 3E-09
25E-10
1 5E-13
60E-11
60E-11
56E 10
74E 11
67E09
36E09
60E-11
33E-13
1 4E-10
14E 10
20E-10
27E-09
60E 11
60E-11
70E-10
27E-09
42E-09
60E-11
t 2E 16
74E 16
9 BE 16
18E 15
1 2E 15
1 4E 14
6 7E 14
96E 16
3 BE 15
5 IE 15
1 6E 14
1 5E 14
1 6F 14


Noncancer
Adult
Dose
(mg/kg-d)
26E 10
2 IE 10
26E 10
21E 10
46E 09
26E 10
26E 10
54E 13
54E-13
1 BE 09
54E 13
1 3E 09
21E-10
26E 10
21E 10
2 1E 10
44E-09
B6E 10
54E 13
21E-tO
2 1E-10
20E-09
26E 10
2 3E-08
1 3E-06
21E-10
1 2E 12
4 BE 10
4 BE 10
7 IE 10
94E09
21E-10
2 IE 10
25E-09
94E-09
t 5E-08
2 1E-10
4 1E 16
26E 15
34E 15
63E 15
42E 15
48E 14
24E 13
34E 15
1 3E 14
1 BE 14
55E 14
5 IE 14
58F 14


Noncancer
Child
Dose
(mg/kg-d)
96E 10
79E 10
96E 10
79E 10
1 7E 08
96E 10
96E 10
20E-12
20E 12
6 BE -09
20E 12
48E09
79E 10
96E-10
79E 10
79E-10
16E-08
32EOT
20E-12
79E 10
79E 10
7 3E-09
97E 10
8 BE 08
4 7E 08
79E 10
43E 12
t BE 09
1 BE 49
27E4J9
35E08
79E 10
79E 10
92E09
35E08
54E 08
79E 10
1 5E 15
97E 15
1 3E 14
24E 14
1 6E 14
1 BE 13
8 BE 13
1 3E 14
49E 14
6 7E 14
20E 13
1 9E 13
? ?E 13


Noncancer
School age
Dose
(mg/kg-d)
58E 10
4 BE 10
5 BE 10
4 BE 10
t OE 08
5 BE 10
5 BE 10
12E 12
1 2E 12
4 IE 09
1 2E 12
29E09
4 BE 10
5 BE 10
4BE-10
4 BE 10
1 OE 08
1 9E09
12E 12
4 BE tO
4 BE 10
44E 09
59E 10
53EOB
29E08
4 BE 10
26E 12
1 IE 09
1 1E09
1 6E 09
2 IE 08
4 BE 10
4 BE 10
5 6E 09
2 IE 08
3 3E 08
4 BE 10
94E 16
59E 15
7 7E 15
1 4E 14
94E 15
1 IE 13
53E 13
76E 15
30E 14
40E 14
1 2E 13
1 2E 13
t IF 13


Noncancer
Farmer
Dose
(mg/kg-d)
26E 10
2 IE 10
26E 10
2 1E 10
46E 09
26E 10
26E 10
54E 13
54E 13
1 BE 09
54E 13
1 3E-09
2 IE 10
26E 10
2 IE 10
2 1E-10
4 4E 09
B6E tO
54E 13
2 IE tO
2 IE 10
20E 09
26E 10
2 3E 06
t 3E 08
2 IE 10
1 2E 12
4 BE 10
4 BE 10
7 IE 10
94E09
2 tE tO
2 tE 10
25E09
94E09
1 5E 08
2 1E-10
4 IE 16
26E 15
34E 15
63E 15
42E 15
4 BE 14
24E 13
34E 15
1 3E 14
1 8E 14
55E 14
5 IE 14
5 BE 14


-------
TABLE 20  Maximum li,. _.ilion Risks and Noncancer HQs In Subarea S2
CHEMICAL
Nttroanlline, 4-
Nttrobenzene
Nltrophenol, 2-
Nrtropheno). 4-
N Nrboso-dl-n butylamine
N-NHroso-dl-n-propylamine
N-Nitrosodlphenylamlne (Dlphenytamlne)
Monachkxoblphanyl
OctachteroWphenyl
Pentachlorobenzene
Pentachlorofalphenyl
PentachloronKrobanzene
Pentaehlorophenol
Phenanthrene
Phenol
Pyrena
Safrola (5-(2-Propenyl)-1 ,3-benzodloxola)
Sryrene
Tetrachloroblphanyl
Tatrachloroethane. 1.1.1 2
Tatrachloroethana, 1.1,2.2-
f etrachloroethene
retraehtorophenol, 2.3.4.6-
Toluene
rrichloro-1.2.2-trifluoroethane, 1.1.2-
frtchlorobenzene. 1.2,4-
frichtoroblphenyl
rrichknoethane, 1,1.1- (Methyl chloroform)
rrtchtoroethane, 1.1.2-
rrichloroethene
frichlorofluorofnelhane
frtchtorophenol. 2.4.5-
rrichlorophenol, 2,4.6-
flnyl acetate
/Inyl chloride
(ylerw. m/p. (m/p-Dimettiyl benzene)
(yfena, o- (o-Dfmethyt benzene)
!.3.7,8-TCOO
,2,3.7,8-PCDD
.2.3.4,7,8-HxCDD
.2.3.6.7,8 HxCDD
,2.3,7.8,9-HxCDD
,2.3,4.6,7.8-HpCDD
XDD
'.3.7.8-TCDF
,2.3.7.8-PCDF
'.3.4.7.8-PCDF
,2.3,4.7.8-HxCDF
.2.36.7.8-HxCDF
',3.4,6.7,8-HxCDF
Inhalation
Slope
Factor
(mg/kg-d)M
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E42
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
10E-02
NA
30E-01
NA
NA
15E+05
7 5E+04
1 5E+04
t 5E«04
1 5E+04
1 5E*03
1 5E»02
1 5E+04
75E»03
75E»04
1 5E+04
1 5E»04
1 5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
002625
NA
0525
0 02625
NF
025
NA
002625
NA
000675
002625
01
75
005
NA
025
00035
NA
0175
00875
NA
0.05
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/Vg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
7 5E-03
NA
15E-01
75E-03
NF
71E-02
NA
75E-03
NA
25E-03
75E-03
2 9E-02
2 1E+00
1 4E 02
NA
7 1E-02
10E-03
NA
50E-02
25E-02
NA
1 4E-02
NA
50E-01
5 OE-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Emission
Rate
(g/sec)
67E-06
55E-06
67E06
55E-08
1 2E-04
67E-06
67E-06
14E4J8
1 4E-08
4 BE -05
1 4E-06
34E-05
55E-06
67E-06
55E-06
55E-08
1 2E-04
23E4K
1 4E-08
55E-06
S5E-06
5 IE-OS
6 BE -06
61E-04
33E-04
55E-OB
30E-08
13E-05
1 3E-05
19E45
25E-04
55E-06
55E-06
64E-05
25E44
3 BE -04
55E-06
108E-11
678E-11
695E-11
1 66E-10
1 09E-10
1 24E 09
6 15E-09
8 77E-11
345E 10
467E-IO
1 4*)F OQ
1 33E-09
1 50E 09
Subarea
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
S2max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
52 max
— 2 m_
,
52 nisx
52 max
52 max
52 max
52 max
52 max
AM
oz max
oZ max
52 max
Adult
Cancer
Risk
NT
NT
NT
NT
32E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E-13
55E-12
51E-13
NT
NT
NT
NT
NT
NT
35E-12
55E-13
NT
NT
2 7E-13
NT
36E-10
NT
NT
80E-12
25E-11
66E-12
1 7P f 1
t *C * 1 1
8 1C 10
1 C • 1 £.
92E 12
45E-12
65E 12
1 3E-11
1 7E 10
IIP in
1 1 1 • 1 U
g or i f
a y t • I i
1 1E-10
Child
Cancer
Risk
NT
NT
NT
NT
80E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-12
14E-11
1 3E-12
NT
NT
NT
NT
NT
NT
B7E-12
14E-12
NT
NT
68E-13
NT
90E-10
NT
NT
2 OE-11
62E-11
1 6E-11
3 1C 11
it-1 1
- nc 1 1
I Ut - 1 1
23E 11
1 IE 11
1 6E-11
32E 11
43E 10
•) cc * t\
t DC 10
7 ec ift
f. DC - lU
2 BE 10
School-age
Cancer
Risk
NT
NT
NT
NT
4 BE -09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-12
83E-12
77E-13
NT
NT
NT
NT
NT
NT
53E-12
82E-13
NT
NT
41E-13
NT
55E-10
NT
NT
12E-11
38E-11
1 OE-11

1 8E-1 1
1 2E-1 1
1 4E 11
6 BE 12
9 BE 12
1 9E 11
2 6E-10

1 6E 1 0
1 5E-10
1 7E 10
Farmer
Cancer
Risk
NT
NT
NT
NT
72E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-12
1 2E-11
1.1E-12
NT
NT
NT
NT
NT
NT
78E-12
1 2E-12
NT
NT
60E-13
NT
81E-10
NT
NT
1 8E-11
56E-11
1 5E-11

2 7E-11
1 BE- 11
20E 11
1 OE 11
1 4E 11
2 BE- 11
38E-10

2 3E • 1 0
2 2E-10
25E 10
                                                                                                                                             Adult      Child    School-age  Farmer
                                                                                                                                           Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HQ        HQ        HO
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
17E-06
2 BE -08
NT
14E-09
2 BE -08
NT
12E-08
NT
28E-08
NT
79E-07
35E08
8 2E-07
59E09
15E-08
NT
67E-09
48E-07
NT
1 9E-07
84E-09
NT
17E-07
NT
29E-08
42E-10
NT
NT
NT
NT
NT
NT
NT
tIT
NT
NT
m
Ml
NT
NT
55E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E-06
1 1E-07
NT
53E-09
1 1E-07
NT
45E-08
NT
1.1E-07
NT
29E-06
1 3E-07
3 IE 06
22E08
55E08
« NT
25E-08
18E-06
NT
70E-07
32E-08
NT
6 4E-07
NT
1 1E-07
16E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
39E-06
63E-08
NT
32E49
63E-08
NT
27E-08
NT
63E-08
NT
18E^»
78E-08
19E-06
13E48
33E-08
NT
15E-06
11E-06
NT
42E07
1 9E-08
NT
39E-07
NT
66E08
95E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 06
28E-OB
NT
14E-09
2 8E-08
NT
12E48
NT
28E-08
NT
79E-07
35E48
8 2E 07
59E-09
1 5E 08
NT
67E09
4 BE -07
NT
1 9E 07
84E-09
NT
1 7E 07
NT
2 9E 08
42E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
olumaV, Appendix V-14
-------
TABLE 20  Maximum Inhalation Risks and Noncancei HQs in Subaipa S2
CHEMICAL
1 2.3.7.8.9 HxCDF
1.2.3.4.6,7.8-HpCDF
1,2.3.4,7,8.9-HpCDF
OCDF
Oioxln TEQ
Mumlnum
toUmony
\ra«nlc
Jarlum
Beryllium
;»dmlum
Chromium (hexavalent)
Chromium (bivalent)
Copper
•ad
forcury (and MeHg)
Itekel
>elenium
.liver
hallium
Inc
lydrogen chloride
otal nitrogen oxides (NOx)
otal sulfur oxides (SOx)
articulate matter
esplrable particulales
Inhalation
Slope
Factor
(mg/kg d)*-1
1 5E»04
1 5E+03
1 5E»03
1 5E+02

MA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0 004375
0004375
ODO0061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E-05
1 3E 03
1 3E-04
1 3E-03
25E-01
NA
NA
2 1E 05
50E 03
1 3E43
1 3E43
1 BE 05
75E 02
50E^>4
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E 09
1 22E 09
1 89E-08
4 28E-08
24E-04
42E-08
37E-05
1 5E-04
33E-08
16E-05
71E47
7 1E-07
94E4>5
43E05
1 4E-03
50E4J6
47E-04
15E45
34E-05
t 2E-04
32E42
24E+00
91E-02
72E^)2
7 2E-02
Subarea
S2 max
S2 max
S2 max
S2 max

52 max
S2max
S2max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 max
S2 m*x
S2 max
S2 max
S2 max
S2 max
S2 max
52 max
S2 max
S2max
Off-site
Vapor
Cone
(ug/m3)
4 IE 11
I 3E-09
1 7E-10
27E-09

34E-05
5 9E-07
52E-06
2 IE-OS
46E 09
22E06
9 9E-OB
99E 08
1 3E 05
80E 06
2 OE 04
7 OE 07
66E05
2 IE 06
4 BE -06
t 7E-05
4 5E 03
3 4E 01
1 3E 02
1 OE 02
10E02
Cancer
Adult
Dose
(mg/kg-d)
1 4E-15
46E-14
60E-15
93E 14
2 1E-13
1 2E 09
2 IE 11
1 8E-10
74E 10
1 6E 13
79E-11
35E-12
35E-12
46E-10
21E-10
69E-09
25E-11
23E-09
74E 11
1 7E 10
59E-10
1 6E-07
1 2E-05
4 5E-07
35E07
3 5E-07
Cancer
Child
Dose
(mg/kg d)
36E-15
1 1E-13
1 5E-14
23E 13
53E-13
2 9E 09
52E-11
45E-10
1 8E 09
4 1E-13
20E-10
87E-12
8 7E-12
1 2E-09
53E-10
1 7E 08
61E-11
58E-09
18E-10
42E 10
1 5E-09
19E-07
30E 05
1 1E-06
8 BE 07
88E-07
Cancer
School-age
Dose
(mg/kg d)
22E-15
69E 14
9 IE-IS
1 4E-13
32E-13
18E^»
3 1E-11
27E-10
1 1E^»
24E 13
1 2E-10
53E-12
53E-12
70E-10
32E-10
1 OE-08
37E-11
35E-09
1 1E-10
25E-10
89E-10
24E-07
18E-05
6 BE -07
53E-07
53E-07
Cancer
Farmer
Dose
(mg/kg d)
32E 15
1 OE 13
1 3E 14
2 IE 13
4 7E-13
26E-09
46E-11
4 IE 10
t 6E-09
36E-13
1 BE 10
78E-12
78E-12
1 OE-09
47E 10
1 5E-08
55E 11
51E-09
16E 10
37E 10
1 3E 09
3 5E 07
27E 05
10E06
79E07
7 9E-07
Noncancer
Adult
Dose
(mg/kg-d)
1 1E-14
36E-13
47E-14
73E-13
1 6E-12
92E09
1 6E-10
14E09
5 BE -09
1 3E-12
61E-10
27E-11
27E-11
36E^9
16E09
54E08
1 9E-10
1 BE 48
58E-10
1 3E 09
46E-09
12E46
93E05
35E-06
2 BE 06
28E46
Noncancer
Child
Dose
(mg/kgd)
42E 14
1 3E-12
1 7E 13
27E-12
6 IE- 12
34E-08
60E-10
53E-09
2 IE 08
4 7E-12
23E 09
1 OE 10
10E-10
1 3E-08
62E09
2 OE-07
72E 10
67E-08
2 1E^»
49E-09
1 7E 08
46E06
35E04
1 3E 05
10E05
1 OE 05
Noncancer
School age
Dose
(mg/kg-d)
25E 14
8 IE 13
1 IE 13
16E-12
37E-12
2 IE 08
36E 10
32E 09
1 3E 08
29E 12
14E 09
6 IE 11
6 IE 11
8 1E-09
37E09
1 2E 07
43E 10
4 IE 08
1 3E-09
29E 09
1 OE 08
2 BE 06
2 IE 04
79E 06
62E 06
62E 06
Noncancer
Farmer
Dose
(mg/kg d)
1 IE 14
36E-13
47E-14
73E-13
16E-12
92E49
1 6E 10
1 4E^)9
58E4J9
1 3E-12
6 IE 10
27E It
27E-11
36E-09
1 6EO9
54EO8
1 9E 10
18E-08
58E-10
1 3E^»
46E-O9
1 2E^)6
93E-05
35E-06
2 BE 06
2 BE 06
 OTES
  NA - Not applicable
  NF * Not found
  NT e No toxlclty Information
  HQ • Hazard quotient
  HI  « Hazard ind«x
  lume V Appendix V 14
-------
                  .\
                        1
TABLE 20  Maximum lni._.-tion Risks and Noncancer HQs in Subarea S2
CHEMICAL
1.2.3.7,8.9-HxCDF
1.2,3.4,6.7.e-HpCDF
1. 2.3.4,7 .B.9-HpCDF
OCDF
DioxInTEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (trivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Paniculate matter
Resplrabte participates
Inhalation
Slope
Factor
(mg/kfl-d)A-1
1 5E»04
t 5E*03
1 5E+03
1 5E+02

NA
NA
50
NA
84
81
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
0.00035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
10E44
75E-05
36E-05
1 3E-03
13E04
13E-03
256-01
NA
NA
2 IE-OS
50E-03
1 3E 03
1 3E-03
1 8E4B
75E-02
50E-04
NA
NA
NA
NF
Emission
Rate
(9/sec)
2 93E-10
930E-09
1 22E 09
1 89E-08
428E-08
24E-04
42E-06
37E-05
15E4M
33E48
18E-05
71E47
71E-07
94E-05
43E-05
1 4E 03
50E-08
47E-04
15E^»
34E-05
1 2E-04
32E-02
24E+00
91E-02
72E^>2
72E-02
Subarea
S2 max
S2 max
S2 max
S2max

S2max
S2max
S2max
S2 max
S2max
S2max
S2max
S2max
S2 max
S2 max
S2max
S2 max
S2max
S2 max
S2max
S2max
S2max
S2 max
S2max
S2 max
S2 max
Adult
Cancer
Risk
22E-11
69E-11
90E 12
14E-11
69E-10
NT
NT
91E-09
NT
1 4E-12
48E-10
14E-10
NT
NT
NT
NT
21E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
54E-11
1 7E-10
22E-11
35E-11
1 7E-09
NT
NT
23E-08
NT
34E-12
12E-09
36E-10
NT
NT
NT
NT
52E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School-age
Cancer
Risk
33E-11
1 OE-10
14E-11
21E-11
10E-09
NT
NT
14E-08
NT
2 IE 12
72E-10
22E-10
NT
NT
NT
NT
31E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
48E-11
1 5E-10
20E-11
31E-11
1 5E-09
NT
NT
20E-08
NT
30E-12
1 1E-09
3.2E-10
NT
NT
NT
NT
46E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                             Adult      Child   School-age   Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ       HQ        HQ       HQ
NT
NT
NT
NT
NT
NT
16E-06
19E-05
16E-04
10E-09
49E-06
22E-06
1 1E-10
NT
NT
25E-03
38E-OB
14E-05
4 6E-07
74E-05
6 IE-OB
25E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E-06
7 IE-OS
60E-04
38E-09
18E-05
8 IE-OS
4 1E-10
NT
NT
9 4E-03
1 4E-07
54E-05
17E06
2 BE -04
2 3E-07
92E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E-06
43E-05
36E-04
23E-09
1 IE-OS
49E-08
25E-10
NT
NT
57E-03
87E48
3 3E-05
10E46
1 7E-04
1 4E-07
556-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E08
19E-05
16E44
10E49
49E-06
22E-08
1 1E-10
NT
NT
25E-03
3 BE -08
14E-05
46E47
74E-05
6.1E-08
25E-03
NT
NT
NT
NT
                                                                               Total Risk    1 SE-08    3 BE-08    2 3E-08    3 4E-08
                                                                                                                                   Total HI    59E-03    2 2E 02    1 3E 02    59E03
 NOTES:
  NA « Not applicable
  NF« Not found       ';
  NT « No toxlclty Information
  HQ « Hazard quotient
  HI  « Hazard Index
 Volume V. Appendix V-14
-------
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                   V    j
 TABLE 2J  Maximum Imitation Risks and Noncancer HQs in Subarea S3


CHEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrylonttrile
Anthracene
Benzene
Benzole acid
Benzotrichtoride
Benzo(a)anthracene
Benzo(a)pyrene
Benzo(b)nuoranlhene
Benzo(g,h.l)perylene
Bearor»(1ooranthen«
Bls(2•
Chrysene
Cresol. m-
Cresol. o- (2-Methyfphenol)
Cresol, p-
Crotonaldehyde
Cumene
DDE. 4.4'-
Dibenz(a.h)anthracene
Dibromochloromethane
Dichlorobenzene, 1 .3-
Dichlorobenzene, 1.4-
Dlchlorobenzene, 1,2-
Dichlorobenzidine, 3.3'-
Dichloroblphenyl
Inhalation
Slope
Factor
(mg/kg-d)"-
NA
NF
77E-03
NA
NA
24E-01
NA
296-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
13E+00
NF
NA
NA
27E-01
NA
81E-02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA


RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0175
00025
00005
0000053
NF
00035
0.005
00175
25
000875
NA
0.07
0004375
NF
NA
004375
0 04375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA

Inhalation
RfD
(mg/kg-d)
1 5E-02
NF
6 4E-04
25E-02
2 5E 02
1 4E-04
75E-02
43E-04
10E«00
NA
NA
NA
NA
NA
NA
NA
NA
10E-02
50E-03
SOE-03
SOE-03
3 BE -04
NA
71E-02
50E-02
71E-04
HE -04
15E-05
NF
10E-03
14E-03
50E-03
71E-01
25E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E-02
1 3E-02
I 3E-03
NA
6 4E-04
NA
NA
50E-03
NA
5 7E 02
1 4E 02
NA
NA

Emission
Rate
(g/sec)
67E-06
30E-04
29E-03
29E-04
20E-04
55E-06
15E-05
1 IE-OS
32E-05
SSE-oe
SSE-OB
SSE-OB
SSE-oe
ssE-oe
87E-00
1 3E-05
67E-OB
37E-05
10E-04
55E-08
49E-04
87E-06
51E-05
55E-06
89E-05
16E-O4
55E-07
67E-08
B7E-OB
55E-08
37E-05
49E-04
2 7E-04
2.5E-04
67E-06
5SE-06
67E-06
55E-06
55E-06
55E-06
55E-06
1 4E-04
55E-06
5 5E-07
55E-06
2 6E-05
55E 06
55E06
55E 06
3 3E 05
4 7E-08


Subarea
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 ma>
S3 max
S3 man
S3 max
S3 max
S3 max
S3 max

Adult
Cancer
Risk
NT
NT
34E-12
NT
NT
71E-11
NT
63E-13
NT
NT
NT
NT
NT
NT
NT
NT
22E-11
NT
NT
NT
31E-14
NT
NT
NT
NT
NT
1 2E-11
1 1E-12
NT
NT
NT
1 5E-1 1
NT
32E-11
23E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT

Child
Cancer
Risk
NT
NT
85E-12
NT
NT
1 8E-10
NT
1 6E-12
NT
NT
NT
NT
NT
NT
NT
NT
54E-11
NT
NT
NT
78E-14
NT
NT
NT
NT
NT
31E-11
2 6E-12
NT
NT
NT
37E-11
NT
79E-11
57E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT

School-age
Cancer
Risk
NT
NT
52E-12
NT
NT
1 1E-10
NT
95E-13
NT
NT
NT
NT
NT
NT
NT
NT
33E-11
NT
NT
NT
4.7E-14
NT
NT
NT
NT
NT
19E-11
18E-12
NT
NT
NT
22E-11
NT
48E-11
34E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT

NT
NT
fit
fir
NT
NT

Farmer
Cancer
Risk
NT
NT
76E-12
NT
n t
NT
1 6E-10
NT
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
48E-I1
NT
NT
NT
70E-14
NT
NT
NT
NT
NT
27E-11
23E-12
NT
n i
NT
NT
33E-11
NT
70E-11
5.1E-12
NT
NT
NT
NT
NT
I » 1
NT
NT
NT
NT


Ml



NT
NT
                                                                                                                                           Adult      Child   School-age  Farmer
                                                                                                                                         Noncancer Noncancer Noncancer Noncancer
                                                                                                                                            HQ       HO       HQ       HQ
S1E-09
NT
54E-06
13E-06
1 3E-07
16E-05
8 4E-10
39E-07
1 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
77E-09
86E-08
24E-07
13E-OB
16E-05
NT
83E-09
13E-09
14E46
13E-05
42E-07
NT
77E^»
44E-08
85E-08
79E^»
12E-08
NT
3 BE -09
51E-08
NT
NT
51E-09
S1E-09
51E4B
NT
9 BE -08
NT
NT
6 1E-08
NT
1 1E 09
44E 09
NT
(IT
19E-08
NT
20E-05
50E-06
50E07
6 IE-OS
32E-09
15E-06
4.9E-10
NT
NT
NT
NT
NT
NT
NT
NT
29E-08
3 2E-07
8 9E-07
47E-08
S9E-05
NT
3 IE 08
47E-09
54E08
4 BE -05
16E-06
NT
29E07
1 7E-07
3 2E 07
29E08
46E-06
NT
4E-08
9E07
NT
NT
9E-08
9E08
9E-07
NT
3 7E 07
NT
NT
23E 07
fJT
4 IE 09
1 7E 08
W
W
1 2E-08
NT
1 2E-05
30E-06
3 OE-07
37E-05
1 9E-09
89E-07
29E-10
NT
NT
NT
NT
NT
NT
NT
NT
17E-08
19E-07
S 4E-07
29E4B
3 BE -OS
NT
19E48
29E-09
32E46
29E-OS
95E-07
NT
1 7E-07
1 OE-07
1 9E 07
18EOB
28E-06
NT
87E-09
1 1E-07
NT
NT
1 IE 08
1 IE 08
1 1E-07
NT
2 2E-07
NT
NT
1 4E 07
NT
25E 09
1 OE-08
NT
m
51E-09
NT
54E-06
1 3E-06
1 3E-07
16E-05
84E-10
3 9E-07
1 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
77E-09
8 6E 08
2 4E-07
13E08
16E-05
NT
83E09
13E-09
14E06
1 3E-05
4 2E-07
NT
7 7E 08
44E-08
8 5E 08
79E09
12E-06
NT
38E-09
51E-08
NT
NT
5 IE 09
5 IE 09
5 IE-OS
NT
98E-08
NT
NT
6 IE 08
NT
1 1E 09
44E 09
NT
MT
Volume V. Appendix V-14
-------
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-------
TABLE 21   Maximum Inhalation Risks and Noncancer HQs in Subaiea S3
CHEMICAL

DichkHodlfluoromethane
Dtchtofoethane, 1,1-(Etti
Dichloroettiane. 1.2-
Dichtoroethene. 1.1- (Vin
Dichtoroethene (bans). 1,2
Dtchtorophenol. 2,4-
Dichtoropropane, 1,2
Dtchtoropropene (els). 1,3-
Dlchlofopropene (trans), 1.3-
Dteihytphthalate
Dlmethoxybenzidine, 3.3'
DIrriethylphenot, 2,4-
Dlnwttiytphthalat*
CN-n-butylphthaMe
CHnHro«olu«rM. 2,8-
Dlnltro-2-methylphenol, 4,6-
Dinttrophenol. 2.4-
Dmttrotolu*n«. 2,4-
CHoxan*.1,4-
CN(n)octy) phthalate
D, 2.4-
Ethyl mcthacrytate
Etfiyi benzene
Ettiyton* dibromlde
Ettiytone oxide
Emylene Ihtoufea
Fluorantnant
Fluorene
Formaldehyde
Furfural
I wptflcnlof
HeptachlwoMphenyl
Hexachtorobenzene
Hexachlorob!phenyl
Hexaehtorobutadlene
Hexechlorocyclohexai
Hexachlorocyclopentadlene
Hexachloroethane
Hexachtorophene
Hexanone, 2-
lndeno(1,2.3-cd)pyrene
Isophoron*
Malefc hydrazlde
Memoxychlor
Methyl-l-butyl ether
Methyl-2-Pentanone. 4- (MIBK)
Melhylene chloride
Methylnaphlhalene. 2-
Monochlofobiphenyl
Naphthalene
Nitroaniline, 2-
Nrtroanihne. 3-
Inhalation
Slope
Factor
(mg/kg-d)"-1
NA
-lidene dichlorlde) NA
91E-02
lldlne chloride) 1 26+00
1- NA
NA
jpylene dichlorlde) NA
1 3E-01
,3- 1 3E-01
NA
NA
NA
NA
NA
NA
6- NF
NA
NA
NA
NA
NA
NA
NA
76E-01
35E-01
NA
NA
NA
45642
NA
456*00
NA
1 66+00
NA
7 BE -02
lamma (Llndane) NA
* NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
\A\BK) NA
1 6E-03
NF
NA
NA '
NA
NF
RAC
(mg/rr>3)
005
0125
NA
0 007075
00175
0 002625
0001
0005
0005
07
NA
00175
NA
0.0875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0.175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0004375
075
002
075
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kgd)
1 4E-02
36E-02
NA
23E-03
50E-03
75E-04
29E-04
14E-03
14E-03
20E-01
NA
50E-03
NA
25E-02
25E-04
NF
50604
50E-04
NA
50E-03
25643
23642
71E-02
14E-05
NA
206-05
10E-02
IDE -02
50642
3 6E-03
1 3E-04
NA
2 OE-04
NA
50E-05
75645
50E06
2 5E-04
75E-05
NF
NA
5 OE-02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E-05
NF
Emission
Rate
(g/sec)
25E-04
1 3E-05
3E-05
3E-05
3E-05
5E-06
3645
3E-05
3645
7E-05
2E-04
55E-08
55E-06
16645
55E-06
55E-06
55648
556-06
4 96 4)4
55E-08
39E-05
25E-04
506-04
1 2E-04
3 IE-OS
t 56-10
556-06
676-06
61E-04
55E-06
55E-07
146-08
5SE-06
1 4E-08
1 06-04
5 5E-05
55E-06
556-06
32E-05
646-05
55E-06
67E-06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
4 2E 05
1 7E 08
55E 06
67E 06
6 7E 06
Subarea
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
Adult
Cancer
Risk
NT
NT
1 7E-12
22E-11
NT
NT
NT
246-12
246-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 36-10
1 66-1 1
NT
NT
NT
406-11
NT
376-12
NT
13E-11
NT
1 2E-11
NT
NT
1 IE-IS
NT
NT
NT
NT
NT
NT
NT
NT
96E 13
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
42E-12
55E-11
NT
NT
NT
606-12
606-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
326-10
396-11
NT
NT
NT
106-10
NT
916-12
NT
336-11
NT
296-11
NT
NT
28E-13
NT
NT
NT
NT
NT
NT
NT
NT
24E 12
NT
NT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
25E-12
33E-11
NT
NT
NT
36E-12
366-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
196-10
246-11
NT
NT
NT
616-11
NT
556-12
NT
20E-11
NT
18E-11
NT
NT
1 7E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 5E 12
NT
Nf
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
37E-12
4.9E-11
NT
NT
NT
536-12
5.36-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
29E-10
356-11
NT
NT
NT
9 06-1 1
NT
81E-12
NT
2.96-11
NT
26E-11
NT
NT
25E-13
NT
NT
NT
NT
NT
NT
NT
NT
? 1E-12
NT
NT
NT
NT
NT
   Adult      Child    School-age   Farmer
Noncancer  Noncancer Noncancer Noncancer
   HQ        HQ        HQ        HQ
2 OE-07
40E-09
NT
64E-08
2 9E-06
8 4E-08
506-07
106-07
106-07
97E-10
NT
1 36-08
NT
726-09
256-07
NT
136-07
1.36-07
NT
136-08
1 86-07
136-07
806-08
936-05
NT
846-11
636419
776-09
146-07
1 86-08
516-08
NT
32E-07
NT
236-05
84646
13645
2 56 07
496-06
NT
NT
1 56-09
1 1648
5 IE 09
6 7E 10
25E 08
2 IE 08
NT
fir
63E 09
54E 06
NT
7 46-07
156-08
NT
2 46-07
1 16 07
326-07
196-06
3 BE -07
386-07
366-09
NT
4.76-08
NT
276-08
95E-07
NT
476-07
476-07
NT
47E08
6 76-07
4 76-07
30607
356-04
NT
3 IE 10
24E08
29E-08
52607
666-08
196-07
NT
12606
NT
87E-05
31605
476-05
95E-07
18E-05
NT
NT
58E09
40E 08
1 9E 08
25E 09
94E 08
79E 08
NT
fK
24E 08
20E 05
NT
4 56-07
916-09
NT
1 4E-07
656-08
1 9E-07
1 1E-06
2 36-07
2 36-07
226-09
NT
29E-08
NT
1 66-08
5 76-07
NT
29647
296-07
NT
29608
40647
2 BE 07
1 86-07
21644
NT
1 9E-10
1 4E 08
1 7E-OB
3 2E 47
40606
1 1E-07
NT
7 IE 07
NT
52E-05
19605
29E05
5 7E 07
1 IE-OS
NT
NT
35E09
24E 08
1 IE 08
1 5E09
57E 08
4 BE 08
NT
NT
1 4E 08
1 ?E 05
NT
2 06 07
406-09
NT
64648
2 96-08
8 46-08
506-07
10647
10647
9 76-10
NT
1 3648
NT
72609
256-07
NT
3647
36-07
NT
3608
86-07
3647
80E08
93E-05
NT
84E-11
63E-09
77E-09
1 4E47
1 BE 08
5 1E-08
NT
3 2E-07
NT
23E05
84606
13E05
2 5E 07
49E-06
NT
NT
1 5E49
1 1E-OB
5 IE 09
67E 10
25E 08
2 1E 08
NT
Nf
63E 09
54E-06
NT
t/oluma V, Appendix V-14
-------
 TABLE 21  Maximum Inhalation Risks and Noncancer HQs in Subaiea S3
CHEMICAL
Nitroaniline. 4-
Nitrobenzene
Nitrophenol. 2-
Nibophenol. 4-
N-NMioso-dl-n-butylamlne
N-NHroso-dl-n-propylamine
N-NHiosodlphenylamlne (Diphenylamlne)
Nonachlofoblphenyt
Octachtorotoiphenyl
Penlachlotobenzene
PentachkHotHphenyl
Pentachkxonrtrobenzene
Pentachlofophenol
Phenanthrene
Pheno)
Pyren*
Safrole (5-(2-Propenyf)-1.3-benzodloxole)
Styrene
rebachloroblphenyl
Tetrachloroelhane. 1.1.1.2-
rebachloro«lh8ne, 1,1.2.2-
retrachloro«lhena
Tetrachlorophenol. 2.3.4.6
Toluene
rrkhkxo-1.2.2-lrifluoroethane. 1.1.2-
rrichtorobenzene. 1 ,2.4-
Trlchloroblphenyl
frkhkxoethane, 1.1,1- (Methyl chloroform)
rrtchtoroethane. 1,1.2-
rrlchlofoethene
rrfchtofofluoromethane
rrtchtoropheno). 2,4,5-
[rlcnlorophenol. 2,4,6-
/Inyl acetate
/inyl chloride
(ylene, m/p- (m/p-Dimethyl benzene)
(ylene, o- (o-Dlmethyl benzene)
!.3.7.8-TCDD
.2.3.7.8-PCDO
,2,3.4. 7.8-HxCDD
.2,3.6.7.8-HxCDO
,2.3.7,8,9-HxCDD
.2.3,4.6,7,8-HpCDD
>CDD
'.3.7.8-TCDF
2.3.7.8PCDF
'.3.4 7.8 PCDF
.2.3.4.7.8 HxCDF
.2.3 6.7.8 HxCDF
'.3.4,6.7.8 HxCDF
Inhalation
Slope
Factor
{mg/kg-d)*- 1
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
2 OE 01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
60E-03
NA
NA
1 OE-02
NA
30E01
NA
NA
1 5E*05
7 5E+04
1 5E»04
1 5E+04
5E+04
5E+03
5E+02
5E+04
5E*03
5E+04
5E»04
5E«04
5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
01
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
15E-01
75E-03
NF
71E-02
NA
75E-03
NA
25E43
29E-02
2 1E+00
1 4E^)2
NA
7 IE 02
1 OE-03
NA
5 OE-02
2 5E 02
NA
1 4E-02
NA
50E01
50E-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
Emission
Rale
(g/sec)
67E06
55E-06
67E06
55E06
1 2E 04
67E-06
67E08
1 4E-08
1 4E-08
48E-05
14E08
34E-05
55E-06
67E-08
55E46
55E-08
1 2E-04
23E-05
14E-08
55E-06
55E-06
5 IE-OS
68E-06
6 1E-04
33E-04
55E-08
30E-06
13E-05
13E-05
19E-05
25E-04
55E-08
55E-06
64E-05
2 5E 04
3 BE -04
55E-06
1 08E-11
67BE-11
B95E-11
1 66E-10
i O.QF in
1 U9C- 1 U
1 24E 09
6 15E-09
8 77E-11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E-09
Subarea
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
c 1 maw
o j fnax
S3 max
S3 max
S3 man
S3 max
S3 max
S3 max
S3 max
S3 man
Off-site
Vapor
Cone
(ug/m3)
2 BE 07
2 3E 07
2 BE -07
23E-07
51E-06
2 BE -07
2 BE -07
59E-10
59E-10
20E-06
59E-10
14E-06
23E-07
2 BE -07
23E-07
23E-07
4 BE -06
95E-07
59E-10
23E07
22E-06
29E-07
14E05
23E-07
1 3E-09
53E-07
7 BE -07
1 OE-05
2 3E-07
27E-06
1 OE-05
16E-05
2 3E-07
45E 13
2 BE 12
3 BE 12
70E 12
A CC 1 t
*< Ot • 1 £
52E 11
26E 10
3 7E 12
1 4E 11
20E 11
60E 11
56E II
63E 11
Cancer
Adult
Dose
(mg/kg-d)
99E-12
81E-12
99E-12
81E-12
1 8E-10
99E-12
99E-12
21E-14
21E-14
70E-11
21E-14
50E-11
81E-12
99E 12
81E-12
81E-12
1 7E-10
33E-11
2 IE 14
81E-12
81E-12
76E-11
10E-11
91E-10
49E-10
81E 12
45E-14
1 8E-11
1 BE- 11
28E-11
36E-10
61E-12
8 IE 12
95E-11
36E-10
56E-10
81E-12
16E-17
1 OE-16
1 3E 16
24E 16
1 6E 16
1 8E-15
91E 15
1 3E 16
5 IE 16
69E 16
2 IE 15
20E 15
22E 15
Cancer
Child
Dose
(mg/kg-d)
25E-11
20E-11
25E 11
20E-11
45E-10
25E-11
25E-11
52E-14
52E 14
1 8E-10
52E-14
1 2E-10
20E-11
25E-11
20E 11
20E-11
42E-10
83E-11
52E-14
20E-11
20E 11
19E-10
25E 11
23E-09
12E09
20E-11
1 1E-13
46E-11
46E-11
69E-11
90E-10
20E-11
20E-11
24E-10
90E-10
14E-09
20E-11
40E-17
25E 16
33E 16
6 IE 16
40E 16
46E 15
2 3E 14
32E 16
1 3E 15
1 7E 15
53E 15
49E 15
55E 15
Cancer
School-age
Dose
(mg/kg-d)
15E-11
2E-11
5E-11
2E-11
7E-10
5E-11
5E 11
31E-14
31E-14
1 1E-10
31E-14
75E-11
12E-11
15E-11
12E 11
1 2E-11
26E-10
50E-11
3 IE 14
2E-11
2E 11
1E-10
5E-11
4E-09
73E-10
12E-11
67E-14
28E-11
28E-11
42E-11
55E-10
12E-11
1 2E-11
1 4E-10
55E-10
85E 10
12E-11
24E 17
15E 16
2 OE-16
37E 16
24E 16
2 BE 15
1 4E 14
20E 16
7 7E 16
1 OE 15
32E 15
30E 15
33E 15
Cancer
Farmer
Dose
(mg/kg-d)
22E-11
1 8E-11
22E-11
18E-11
40E-10
22E-11
22E-11
46E-14
46E-14
1 6E-10
46E 14
1 IE 10
18E-11
22E-11
1 8E-1 1
18E-11
3 BE 10
74E-11
46E-14
18E-11
18E 11
1 7E-10
22E-11
20E09
1 1E-09
18E-11
99E-14
4 IE 11
4 IE-It
61E-11
8 IE 10
18E-11
18E-11
21E-10
8 IE 10
12E09
18E-11
35E-17
22E-16
29E-16
54E-16
36E 16
4 IE 15
20E 14
29E 16
1 IE 15
1 5E 15
4 7E 15
44E 15
49E 15
Noncancer
Adult
Dose
(mg/kg-d)
77E-11
63E 11
77E-11
63E-11
1 4E-09
77E-11
77E-11
1 6E-13
16E 13
55E-10
16E-13
39E 10
63E-11
77E-11
63E-11
63E-11
1.3E-09
26E-10
1 6E-13
83E-11
63E-11
59E-10
78E-11
70E-09
3 BE -09
63E-11
35E-13
1 4E-10
1 4E-10
2 IE 10
2 BE 09
63E-11
63E 11
74E-10
2 BE 09
44E09
63E-11
1 2E-16
78E-16
10E-15
1 9E 15
1 3E-15
1 4E 14
7 IE 14
1 OE 15
40E 15
54E 15
1 6E 14
1 5E 14
1 7E 14
Noncancer
Child
Dose
(mg/kg-d)
29E-10
24E 10
29E-10
24E-10
52E-09
29E-10
29E-10
60E-13
60E 13
20E09
60E-13
14E-09
24E-10
29E 10
24E-10
24E-10
97E-10
60E-13
24E 10
24E-10
22E-09
29E-10
26E08
1 4E-08
24E-10
1 3E-12
54E 10
54E 10
80E-10
1 IE-OB
24E-10
24E-10
2 BE 09
1 IE 08
1 6E 08
24E 10
46E-16
29E 15
38E-15
7 IE 15
4 7E 15
53E 14
26E 13
3 BE 15
1 5E 14
20E 14
6 1E 14
5 7E 14
65E 14
Noncancer
School-age
Dose
(mg/kg-d)
1 7E-10
1 4E-10
1 7E-10
1 4E-10
31E-09
1 7E-10
1 7E-10
36E-13
36E-13
1 2E-09
36E-13
88E-10
1.4E-10
1 7E-10
1 4E-10
1 4E 10
30E09
58E-10
36E-13
4E 10
4E-10
3E-09
BE 10
6E08
86E-09
1 4E-10
78E-13
32E-10
32E-10
48E-10
64E09
1 IE 10
1 4E-10
1 7E-09
64E09
99E-09
1 4E-10
28E-18
18E 15
23E-15
43E 15
28E-15
32E 14
1 6E 13
23E 15
90E 15
1 2E 14
37E 14
35E 14
39E 14
Noncancer
Farmer
Dose
(mg/kg-d)
77E-11
63E 11
77E 11
63E-M
1 4E 09
77E-11
77E 11
16E-13
16E-13
55E 10
16E-13
39E 10
83E 11
77E-11
83E-11
63E 11
1 3E-09
26E-10
16E-13
63E-11
63E-11
59E-10
78E-11
70E-09
3 BE -09
63E-11
35E-13
1 4E 10
1 4E-10
2 IE 10
2 BE -09
63E 11
63E-11
74E 10
28E49
44E 09
63E-11
12E 16
7 BE 16
10E 15
1 9E 15
13E 15
14E 14
7 IE 14
1 OE 15
40E 15
54E 15
1 6E 14
15E 14
1 7E 14
olume V. Appendix V-14
-------
TABLE 21  Maximum li...Cation Risks and Noncancer HQs in Subarea S3



CHEMICAL
Nittoanlline. 4-
Nttrobenzene
NHrophenol. 2-
Nrtrophenol. 4-
N Nrboso-dl-n-butylamlne
N Nltroso-dl-n-propylamlne
N-NHrosodlphenylamln* (Dtphenytamlne)
Nonachloroblphenyl
Oclachlofobipnenyl
PentachkHobenzene
Pentachfcxoblphenyl
PentachloronHrobenzen*
PentacMorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyf)-t.3-benzodloxole)
Styiene
Tetrachtoroblphenyl
Tetrachtoroetfiane, 1.1,1,2-
Tetrachkxoethane. 1,1,2,2-
Tetrachloroettiene
Tetrachlorophenol, 2.3,4,6-
Toluene
Trichloro-1.2.2-1rMuoroethane, 1.1,2-
Trkhlorobefizene. 1.2,4-
TrtchlwoHphenyl
Trtchloroethane. 1.1.1- (Methyl chloroform)
Trlchloroethene. 1.1,2-
Trichicfoethene
Trfchkwofluoromethane
Trichlorophenol. 2.4,5-
rriehlorophenol. 2.4.6-
i/lnyl acetate
iflnyl chloride
Kylene, m/p- (m/p-Dlmettiyl benzene)
Xylene, o- (o-CNmethyl benzene)
Z,3.7,8-TCDD
1,2.3.7,8-PCDO
l.2.3.4.7.B-HxCDO
1.2.3,6,7.8-HxCDO
1.2,3,7.8.9-HxCDO
1,2,3.4.6,7.8-HpCDO
3CDD
!.3.7.8-TCDF
1,2.3.7,8 PCDF
Z.3.4.7.8-PCDF
1, 2.3.4. 7.8-HxCDF
l.2.3.6.7.8-HxCDF
?,3.4.6.7.8-HxCDF
Inhalation
Slope
Factor
-------
TABLE 21  Maximum Inhalation Risks and Noncancet HQs in Subarea S3
CHEMICAL
1.2.3,7.8,9-HxCDF
1.2,3.4,8,7.8-HpCDF
1.2.3,4,7,8.9-HpCDF
OCDF
   CNoxIn TEQ
Aluminum
AnBmony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
ttwcury (and MeHg)
Selenium
JHver
Thallium
'.inc
 tydrogen chloride
 otal nitrogen oxides (NOx)
 otal sulfur oxides (SOx)
 'articulate mailer
 tesplraMe parttculates
Inhalation
Slope
Factor
(mg/kg-d)A- 1
1 5E+04
1 5E»03
1 5E+03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
OOO4375
0000438
0004375
0875
NA
NA
0000075
0.0175
0004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
36E05
13E-03
13E04
13E-03
25E-01
NA
NA
2 IE-OS
50E-03
13E03
1 3E-03
1BEO5
75E-02
SOE-04
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
930E09
1 22E-09
1 89E 08
428E-08
24E-04
42E-OS
37E-05
15E-04
33EOB
16E-05
71E-07
71E-07
94E-05
43E-05
14E-03
50606
47E04
15EO5
34EO5
1 2EO4
32E02
24E+00
91EO2
72E02
72E02
Subarea
S3 max
S3 max
S3 max
S3 max

S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
S3 max
Off site
Vapor
Cone
(ug/m3)
1 2E-11
39E 10
5 IE 11
80E-10

10E-05
1 8E-07
16E-06
63EO6
14E-09
87EO7
30EO8
30EO8
39EO6
18E06
59E05
2 1E-07
20E05
83E07
1 4EO6
50EO8
13E03
lOE-Oi
38EO3
30E-03
30EO3
Cancer
Adult
Dose
(mg/kg-d)
43E-16
1 4E-14
1 BE 15
28E-14
63E 14
35E-10
62E 12
55E-11
22E-10
49E 14
24E-11
10E-12
106-12
1 4E-10
64E-11
21E09
7 4E-12
70E-10
22E-11
50E-11
1 8E-10
47E08
36EO8
1 3E-07
1 1E-07
1 1E07
Cancer
Child
Dose
(mg/kg-d)
1 1E-15
34E 14
45E-15
70E-14
16E-13
8BE-10
15E-11
1 4E-10
55E-10
1 2E 13
59E-11
26E-12
2 6E-12
35E-10
1 6E-10
52E-09
18E-11
17E-09
55E-11
1 3E-10
44E-10
12E07
89EO6
34E07
27E07
27EO7
Cancer
School-age
Dose
(mg/kg-d)
65E-16
2 1E-14
27E-15
42E-14
95E-14
5 3E-10
94E-12
82E-11
3 3E-10
73E-14
36E-11
1 6E-12
1 6E-12
2 1E-10
96E-11
31EO9
1 1E-11
10E-09
33E-11
76E-11
2 7E-10
71E08
54E06
20E07
16EO7
16EO7
Cancer
Farmer
Dose
(mg/kg-d)
96E-16
31E-14
40E-15
62E-14
1 4E-13
79E-10
1 4E-11
1 2E-10
49E-10
1 1E-13
53E-11
23E-12
23E-12
31E-10
1 4E-10
46E-09
16E-11
15EO9
49E-11
1 IE-ID
39E-10
1 1E-07
80E06
30EO7
2 4EO7
24E07
Noncancer
Adult
Dose
(mg/kgd)
34E 15
1 IE 13
1 4E 14
22E-13
49E-13
2 BE 09
4 BE 11
4 3E-10
1 7EO9
3 BE 13
1 BE 10
02E-12
82E-12
1 1E09
49E-10
16EO8
5 BE 11
54E-09
1 7E-10
39E-10
14EO9
37E07
2 BE 05
10E06
83E07
83EO7
Noncancer
Child
Dose
(mg/kg-d)
13E-14
40E-13
52E-14
81E-13
1 8E-12
10E-08
1 6E-10
16E-09
64EO9
1 4E-12
69E-10
31E-11
31E-11
40E-09
18E-09
80E08
2 1E-10
20EO8
6 4E-10
15E09
52E09
14EO6
10E04
39E06
31E06
31EO8
Noncancer
School-age
Dose
(mg/kg-d)
76E-15
24E-13
32E-14
49E-13
1 1E-12
82EO9
1 1E-10
96E-10
39EO9
86E-13
42E-10
18E-11
18E 11
24E09
1.1EO9
36EOB
1 3E-10
1 2E-08
39E10
8 BE-10
31EO9
83E-07
63E05
24E06
19E06
19E-06
Noncancer
Farmer
Dose
(mg/kg-d)
34E-15
1 1E-13
1 4E-14
22E 13
49E-13
2 BE 09
4 BE 11
43E 10
1 7EO9
38E-13
1 BE-10
8 2E-12
82E-12
1 1EO9
49E-10
16EOB
56E-11
54E09
1 7E-10
39E-10
1.4EO9
37E07
2 BEOS
10E08
83E07
83E07
 IOTE5:
  NA-NotappHcable
  NF « Not found
  NT • No toxtelty (nformadpn
  HO - Hazard quotient   '
  HI -HazardIndex
  lumeV. Appendix V-14
-------
TABLE 21  Maximum ln>..,d(ion Risks and Noncancer HQs in Subarea S3
CHEMICAL
1.2,3,7.8.9-HxCDF
1,2,3.4.6,7.8-HpCDF
1.2,3.4,7,8.9-HpCDF
3CDF
  Dloxln TEQ
Uumrnum
Vntimony
toenfc
iarturn
Chromium (hexavalent)
^hromhifii (Uivalent)
 •ad
•torcury (and MeHg)
>flck«l
ielenhjm
>Nvef
Thallium
line
Vdrog«n chloride
'otel nitrogen oxides (NOx)
 otal sulfur oxktos (SOx)
'articulate matter
iesptrabl* particulates
Inhalation
Slop*
Factor
(mg*g-d)A-1
1 5E+04
1 5E+03
1 5E+03
1 5E+02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF


RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000283
0.000125
0.004375
0.000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF

Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
10E-04
75E-05
38E-05
13E-03
13E-04
13E-03
2.5E-01
NA
NA
2 IE-OS
50E-03
13E-03
1 3E-03
18E-05
75E-02
5DE-04
NA
NA
NA
NF

Emission
Rate
7
22E4)5
1BE-08
74E-04
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1BE-08
2 IE-OS
18E-04
11E-09
5.5E-06
24E-08
1 2E-10
NT
NT
28E-03
43E-08
16E«
52E-07
84E-05
69E-08
2 BE -03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1.1E-08
13E-05
1 1E-04
69E 10
33E-06
15E-06
74E-11
NT
NT
17E-03
26E-08
9 BE ^6
3.1E-07
50E-05
42E-08
1.7E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
48E-07
57E06
4 BE -05
30E-10
15E-06
65E-09
33E-11
NT
NT
75E4M
12E-08
43E06
1 4E-07
22E45
16E-08
74E-04
NT
NT
NT
NT
                                                                                Total Risk   4 6E-09    1 2E-08    7 OE-09    1 OE-OB
                                                                                                                                     Total HI    1 8E-03    66E-03    40E-03   1 BE-03
JOTES.
  NA - Not appllcabt*
  NF - Not found        x;
  NT - No toxtcity IntormatJon
  HQ - Hazard quotient
  HI  -HazardIndex
 olume V, Appendix V-14
-------
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-------
  TABLE 22  Maximum Inha.alion Risks and Noncanccf HQs in Subarea Wl



"HEMICAL
Acenaphthene
Acenaphthylene
Acetaldehyde
Acetone
Acetophenone
Acrytonftrtle
Anthracene
Benzene
Benzole acid
Benzotrichloride
3enzo(a)enthracene
Benzojajpyrene
B«nzo(b)fluoranthene
Benzo(g,h.l)perylene
Benzo(k)fluorarithene
Bls(2-chtoroelhoxy) methane
Bls(2-chk>roethyl)ether
Bls(2-chloro(sopropyf)ether
Bis(2-elhylhexyl)phltialate
Bromodichloromethane
Bromoform
Bromomethane
Bromodlphenyl ether, p-
Butonone, 2- (Methyl ethyl ketone)
Butyfbenzytphlhalate
Carbon dlsulfide
Carbon letrachlorlde
Chtordarte
Chloro-3-methytprxmol. 4
Chloroanlllne. p- (4-Chloroanlllne)
CMorobenzene
ChlorobenzHate
Chlotoethane (Ethyl chloride)
Chloroform
Chtoromethane
Chloronaphthalene, beta
Chlorophenol, 2-
Chlofodlphenyl ether, 4- '
Chrysene
Cresol. m-
Cresol, o- (2-Methylphenol)
Cresol, p-
Crolonaldehyde
Cumene
DDE. 4,4'-
Dibenz(a,h)anlhracene
Dibromochloromethane
Dlchlorobenzene. 1 .3-
Dichlotofaenzene. 1 .4-
Dichlotobenzene, 1.2-
Dtchlorobenzidine. 3,3'-
Dic hlorob iphenyl
Inhalation
Slope
Factor
5
67E-08
37E4K
10E-04
SSE^B
49E-M
87E-08
5 IE-OS
55E-08
89E-OS
16E-04
55E-07
67E4M
67E-OB
55E-OB
37E-05
49E-04
2 7E-04
25E-04
67E-06
55E-06
67E-06
55E-06
55E06
55E-06
55E06
1 4E-04
5SE-06
55E 07
55E06
26E 05
55E06
55E 06
55E06
33E 05
4 7E 08



Subarea
Wl max
Wl max
Wlmax
Wt max
Wl max
Wl max
Wl max
Wl max
Wlmax
Wt max
Wt max
Wt max
Wlmax
Wt max
Wl max
Wl max
Wl max
Wl max
Wl max
Wl max
Wlmax
Wt max
Wl max
Wt max
Wt max
Wl max
Wl max
Wl max
Wlmax
W1 max
Wl max
Wlmax
Wl max
Wt max
Wl max
Wl max
Wlmax
Wl max
Wl max
Wl max
Wl max
Wl max
Wt max
Wl max
W1 max
Wl max
Wl max
Wl max
Wl max
Wl max
Wl ma*
Wl max

Adult
Cancer
Risk
NT
NT
48E-11
NT
NT
10E-09
NT
89E-12
NT
NT
NT
NT
NT
NT
NT
NT
306-10
NT
NT
NT
44E-13
NT
NT
NT
NT
NT
1 7E-10
15E-11
NT
NT
NT
2 1E-10
NT
45E-10
32E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT

Child
Cancer
Risk
NT
NT
1 2E-10
NT
NT
25E-09
NT
22E-11
NT
NT
NT
NT
NT
NT
NT
NT
76E-10
NT
NT
NT
1 1E-12
NT
NT
NT
NT
NT
4 3E-10
37E-11
NT
NT
NT
52E-10
NT
1 1E-09
80E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT

School-age
Cancer
Risk
NT
NT
72E-11
NT
NT
1 5E-09
NT
1 3E-11
NT
NT
NT
NT
NT
NT
NT
NT
46E-10
NT
NT
NT
68E-13
NT
NT
NT
NT
NT
26E-10
2 2E-1 1
NT
NT
NT
3 1E-10
NT
6 7E-10
4BE-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT

Farmer
Cancer
Risk
NT
NT
1 1E-10
NT
NT
22E-09
NT
20E-11
NT
NT
NT
NT
NT
NT
NT
PI i
NT
68E-10
NT
NT
NT
98E-13
NT
NT
NT
NT
NT
38E-10
33E-11
NT
NT
NT
46E-IO
NT
99E-10
7 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                           Adult      Child   School-age  Farmer
                                                                                                                                         Noncancer Noncancer Noncancer Noncancer
                                                                                                                                            HO       HQ       HQ       HQ
72E-O8
NT
76E-05
19E-05
19E-06
2 3E-04
12E-OB
55E-06
18E-09
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-07
12E-06
33E-08
tflE-07
22E-04
NT
12E^)7
18E-08
20E-05
18E-04
59E-06
NT
1 IE-OS
62E-07
12E-06
1 1E-07
17E-05
NT
54E46
71E-07
NT
NT
71E-08
7 tE-08
71E-07
NT
ME -06
NT
NT
BSE 07
NT
16E 08
62E 08
NT
NT
27E-07
NT
28E04
70E^5
7 IE-OS
6 5E-04
44E-08
2 IE-OS
68E-09
NT
NT
NT
NT
NT
NT
NT
NT
40E-07
45E-06
1 2E-05
6 6E-07
83E-04
NT
43E-07
S6E-08
7.5E05
67E-04
22E45
NT
40E-06
23E-06
44E-06
41EW
64E-05
NT
2 OE 07
27E-06
NT
NT
2 7E 07
2 7E 07
27EO6
NT
52E08
NT
NT
32E 06
NT
58E 08
23E 07
NT
m
16E-07
NT
1 7E-04
42E-05
43E-06
5 2E-04
2 7E-OB
13E-05
41E-09
NT
NT
NT
NT
NT
NT
NT
NT
2 4E 07
27E-06
75E^)6
40E07
SOE4M
NT
2 6E-07
40E08
46E05
40E04
1 3E-O5
NT
24E-06
1 4E-06
27E06
2 5E-07
39E-05
NT
1 2E-07
16E-06
NT
NT
t 6E 07
1 6E 07
16E-06
NT
3 IE 06
NT
NT
1 9E 06
NT
35E 08
t 4E-07
NT
NT
72E-08
NT
76E-05
19E-05
19E-08
23E-04
12E08
55E-06
18E-09
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-07
12E-06
33E46
18E-07
22E-04
NT
1 2E 07
1BE-08
20E05
18Efl4
59E-06
NT
t IE 4)6
62E47
12E06
1 IE 07
1 7E-05
NT
54E08
7 1E-07
NT
NT
7 IE 08
7 IE 08
7 IE 07
NT
1 4E-06
NT
NT
85E^)7
NT
t 6E 08
6 2E 08
NT
NT
Volume V. Appendix V-14
-------
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-------
  TABLE 22  Maximum In.   'ion Risks and Noncancer HQs in Subarea W1
CHEMICAL
Dichlorodifluoromethane
Dichloroethane. (.1- (Ethylidene dichloride)
I CNchloroethan*. 12
Dichloioethene. 1.1- (Vmylidme chloride)
Oichloioctton* (trans). 1 .2-
Dichlorophenol. 2.4-
j Dlchloropropane. 1,2- (Propylene dichloride)
| Dichloropropene (els) 1.3-
Olchloropropone (bans), 1.3-
Dlemytphlhalate
Dim«thoxyb«nzidin«. 3.3'-
Dlmethytpheno), 2.4-
3lm»thytphthalale
31 n butylphthalate
3lnrtroto)u«ne. 2.6
Dlnrbo-2-m«thy1phenol. 4.6-
Dlnttrophenot. 2,4-
Dlnrtiotoluene. 2,4-
Dloxana, 1.4
3l(n)octy1 phthalale
3, 2.4-
Ethyt methacrylate
Ethylbonzan*
tthyiene dibromide
ithytene oxide
Ethytene thlourea
-luoranthene
-luorene
formaldehyde
Furfural
Hcptochlor
leptachlorobiphenyl
Haxachforobenzene
•lexachlorobiphenyt
Hexachlorob'jtadiene
Hexachlotocyclohexane, gamma (Llndane)
Hexachlorocyclopentadiene
texachloroelhane *
H8»achloroph«n»
Hexanona, 2-
ndeno(1 ,2.3-cd)pyrene
sophorona
Maleic hydtazida
Wettioxychlor
Wethyt (-butyl ether
Wethyt-2-Pentanone. 4- (MIBK)
Methylene chloride
Methytnaphthalene, 2-
Monochlorobrphenyl
Naphthalene
'Mioanilme 2
Mrtroanihne. 3-
Inhalation
Slope
Factor
(mfl/kg-d)«-
NA
NA
9 1E-02
1 2E»00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E400
NA
7 8E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E 03
NF .
NA
NA
NA
NF
RAC
(mg/m3)
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
000005
NF
Inhalation
RID
(mg/kg-d)
1 4E 02
3 6E-02
NA
2 3E 03
50E-03
7 5E-04
29E 04
1 4E-03
1 4E 03
20E-01
NA
50E-03
NA
25E 02
NF
50E 04
50E 04
NA
5 OE 03
2 5E 03
23E 02
7 1E 02
1 4E-05
NA
20E 05
1 OE 02
1 OE 02
50E 02
36E03
1 3E-04
NA
2 OE-04
NA
50E-05
75E 05
50E 06
2 5E-04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 IF 01
NF
NA
1 OE 02
1 4F. 05
NF
Emission
Rate
(g^sec)
25E44
3E45
3E05
3E^K
55E-06
3E 05
3E4S
3EXJ5
7E-05
2E-04
55E-06
1 6E-05
55E-06
55E-06
55E-06
55E-06
49E04
50EXM
1 2EW
1 5E 10
8 7E46
6 1EO4
1 4EO8
55E06
1 OE4M
55E 05
55E 06
55E 06
3 2E OS
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
t 3E 05
4 OE 04
4 2E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
W1 max
Wl max
Wl max
Wl max
Wl max
Wl max
Wt max
Wt max
Wl max
Wl max
Wl max
Wl max
W1 max
W1 max
Wl max
Wl max
Wt max
Wl max
Wl max
Wl max
Wl max
Wl max
W1 max
W1 max
Wl max
Wl max
Wl max
Wt max
Wl max
Wl max
Wl max
Wl max
Wl max
Wl max
W1 max
Wt max
Wt max
Wl max
Wl max
W1 max
Wl max
Wl max
Wl ma>
Wl max
Wl ma<
Wl ma«
Wl ma.
Wl rra.
Wl ma.
Wl ma«
Wl ma«
W1 ma.
Adult
Cancer
Risk
NT
NT
2 4E-11
3 1E-10
NT
NT
NT
34E-11
34E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 BE -09
22E-10
NT
NT
NT
57E-10
NT
51E-11
NT
1 8E-10
NT
1 6E-10
NT
NT
1 6E-12
NT
NT
NT
NT
NT
NT
NT
tn
i 4r 1 1
tn
in
in
in
in
Child
Cancer
Risk
NT
NT
59E 11
78E 10
NT
NT
NT
84E 11
84E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
45E 09
55E-10
NT
NT
NT
1 4E 09
NT
1 3E-10
NT
46E-10
NT
4 tE-10
NT
NT
40E 12
NT
NT
NT
fJT
fJT
NT
NT
in
34! II
in
tn
tn
in
NT
School age
Cancer
Risk
NT
NT
36E 11
47E-10
NT
NT
NT
51E-11
51E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
27E09
33E-10
NT
NT
NT
B5E-10
NT
77E-11
NT
I » I
28E-10
NT
25E-10
NT
NT
24E 12
tlT
tlT
NT
NT
NT

n r
I J T
2 Ot 11
in
in
i j t
in
in
Farmer
Cancer
Risk
NT
NT
53E-I1
69E-IO
NT
NT
NT
75E-11
75E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
40E-09
49E-10
NT
NT
NT
1 36-09
NT
n t
1 1E-10
WT
rl 1
A 1E-10
NT
36E-10
NT
NT
36E-12
KIT
W 1
NT
MT
HI
NT
H T
M 1

•i fip i i
j \*r 11
r i T

f j r
m
                                                                                                                                                Adult     Child   School age   Farmer
                                                                                                                                             Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                HQ       HO       HQ       HQ
28E 06
5 7E-08
NT
90E-07
40E 07
1 2E 06
7 1E 06
1 4E 06
1 4E 06
1 4E-08
NT
1 8E-07
NT
1 OE 07
36E-06
NT
18E06
1 8E-06
NT
1 BE 47
25E^»
18E-06
1 IE 06
1 3E-03
NT
12E09
89E08
1 1E 07
20E06
25E 07
7 1E-07
NT
44E-06
NT
3 3E-04
1 2E 04
1 BE 04
36E06
69E 05
NT
NT
22E 08
15E 07
7 1E 08
94E 09
3 fit 07
3 OF 07
tn
tn
8 9E 08
? r,l m
tn
1 OE 05
2 IE 07
NT
34E 06
1 5E 06
44E06
26E 05
53E06
53E-06
5 1E-08
NT
66E-07
NT
3 8E 07
1 3E-05
NT
66E06
66E-06
NT
66E47
94E06
66E46
42EO6
49E43
NT
44E 09
3 3E 07
4 OE-07
73E 06
93E 07
27E06
NT
1 7E-05
NT
1 2E03
44E 04
66E 04
1 3E 05
2 6E 04
NT
NT
8 IE 08
56E 07
2 n 07
3 5E 08
1 ir 06
1 It Of,
in
tn
3 JF 1)7
? fit 04
rn
63E 06
1 3E-07
NT
20E-06
91E 07
2 7E 06
1 6E 05
32E 06
32E 06
3 1E-08
NT
4 OE-07
NT
2 3E 07
80E06
NT
40E06
40E-06
NT
40E 07
57E06
40E06
25E06
29E 03
NT
27E09
20E07
24E 07
44E 06
56E 07
16E 06
NT
10E 05
NT
74E 04
27E04
40E 04
80E 06
1 BE 04
NT
NT
49E 08
34E 07
1 RE 07
2 IF 08
8 OF 07
R n 07
tn
Ml
? OF. 07
1 ?f 04
fit
28E06
5 7E 08
NT
90E07
40E 07
1 2E 06
7 IE 06
1 4E 06
1 4E 06
1 4E-08
NT
1 BE -07
NT
1 OE 07
36E 06
NT
1 BE 06
1 BE -06
NT
1 BE 07
25E06
1 8E 06
1 IE 06
1 3E 03
NT
1 2E 09
89E 08
1 IE 07
20E 06
25E 07
7 IE 07
NT
44E 06
NT
33E 04
1 2E 04
1 BE 04
36E 06
69E 05
NT
NT
72E 08
15E 07
7 1E 08
94F 09
3f>E 07
3 OF 07
NT
NT
89F 08
7 r,r 05
in
Volume V. Appendix V 14
-------
TABLE 22  Maximum Inhalation Risks and Noncancpi HQs in Subniea W1
CHEMICAL
Niboanlhne. 4
Mitiobenzene
litiophenol, 2-
litiophenol. 4-
-4 Nrtiosc-dl n butytamln*
4 Ntooso-dl n piopytamine
4 Nitrosodiphenylamine (Diphenylamme)
Jonachloroblphenyt
)ctachlorobipheny1
'entachloroberurene
'entachlorobiphenyl
'•ntachloronrtrobenrene
"entachtorophenol
'henanthrene
'henol
yen*
~ .afrole (5-(2-Pfopenyl) 1.3 benzodioxole)
'tyrene
.; elrachlofobiphenyl
: etrichloroethane, t.t.t 2-
i etrachloroethane. 1.1,2,2
3 etrachloroethene
i ebachlorophenol. 2.3.4.6
1 oluene
richk>ro-1,2,2-bifluoroethan« 1 1.2
; tlchloiobenzene. 1,2,4-
ilchtoiobtphenyl
richlorovthane, 1,1,1- (Methyl chloioloim)
richloroethane. 1,1,2-
rkhloroethene
ftehtofonuoromethane
\ Ichtorophenol. 2.4.5-
Ichtofophenol. 2.4,6
nyt acetate
nyt chloride
font, m/p- (m/p-Dlmethyl benzene)
dene, o- (o-Dimethyl benzene)
Inhalation
Slope
Factor
(mg/kgd)" 1
NF
NA
NF
NF
54E«00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E 02
20E 01
2 OE-03
NA
NA
NA
NA
NA
NA
57E 02
6 OE-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
002625
0 1
7 5
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E-04
7 5E-03
NA
15E 01
7 5E-03
NF
7 1E 02
NA
75E 03
NA
25E 03
7 5E 03
2 9E 02
2 1E»00
1 4E 02
NA
7 1E 02
10E 03
NA
50E 02
2 5E-02
NA
1 4E-02
NA
50E 01
50E 01
Emission
Rate
(g'sec)
6 7E 06
55E 06
67E 06
55E06
1 2E 04
67E06
67E-06
1 4E-08
1 4E-08
4 BE -05
1 4E 08
34E05
55E 08
67E 06
55E4W
55E-06
1 2E 04
23E 05
1 4E 08
55EXJ6
55E 06
5 IE 05
68E 08
6 IE 04
3 3E 04
55E 06
30E 08
1 3E 05
1 3E05
19E05
2 5E 04
55E 06
55E 06
64E 05
2 5E 04
3 BE 04
55E06
Subarea
Wl max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
Wl max
Wl max
Wl max
Wl max
Wl max
W1 max
Wl max
Wl max
W1 max
Wl max
W1 max
W1 max
W1 max
Wl max
Wl max
Wt max
Wl max
Wl max
W1 max
Wl max
Oft site
Vapor
Cone
(ug/m3)
39E 06
32E 06
39E 06
32E 06
7 1E05
39E 06
39E06
83E 09
83E 09
2 BE 05
83E 09
20E 05
32E-06
39E 06
32E 06
32E 06
6 BE 05
1 3E 05
83E09
32E06
32E 06
30E05
40E-06
36E-04
1 9E 04
32E06
1 BE -08
74E06
7 4E 06
1 1E 05
1 4E 04
32E 06
32E 06
3 BE 05
1 4E 04
2 2E 04
32E 06
Cancer
Adult
Dose
(mg/kg d)
1 4E 10
1 IE 10
1 «E 10
1 1E-10
25E 09
1 4E-10
1 4E-10
29E 13
29E-13
99E-10
29E 13
70E-10
1 1E-10
1 4E-10
1 1E-10
1 IE 10
24E 09
4 7E-10
29E 13
1 1E-10
1 IE 10
1 IE 09
1 4E 10
1 3E 08
6 9E-09
1 IE 10
63E 13
26E 10
26E-10
39E 10
5 1E 09
1 IE 10
1 IE 10
1 3E 09
5 1E 09
7 9E 09
1 1E-10
Cancer
Child
Dose
(mg/kg-d)
35E 10
2 BE 10
35E 10
2 BE 10
6 3E 09
35E 10
35E 10
72E 13
72E 13
25E 09
72E 13
1 7E-09
2BE-10
35E-10
28E-10
28E-10
60E 09
1 2E 09
72E-13
28E-10
28E-10
2 7E 09
35E-10
3 2E-08
1 7E 08
28E-10
16E-12
65E-10
65E-10
96E-10
1 3E-08
2BE-10
2 BE 10
33E-09
1 3E 08
2 OE-08
28E-10
Cancer
School age
Dose
(mg/kgd)
2 1E-10
1 7E 10
2 IE 10
1 7E 10
3 BE 09
2 1E-10
2 IE 10
44E 13
44E 13
1 5E-09
44E-13
1 1E-09
1 7E-10
2 1E-10
1 7E-10
1 7E-10
36E 09
70E-10
44E-13
7E-10
7E-10
6E09
1E-10
9E08
OE08
7E-10
94E-13
39E-10
39E-10
58E-10
77E-09
1 7E-10
1 7E-10
20E-09
77E09
1 2E-08
1 7E-10
Cancer
Faimer
Dose
(mg/kg d)
3 IE 10
25E 10
3 IE 10
25E 10
56E09
3 1E 10
3 IE 10
65E-13
65E-13
2 2E-09
65E 13
1 6E 09
25E-10
3 1E-10
25E-10
25E 10
5 3E 09
10E-09
65E 13
25E-10
25E 10
24E09
3 1E 10
2 8E 08
1 5E 08
25E-10
1 4E 12
5 BE 10
58E-10
86E-10
1 1E-08
25E 10
25E-10
30E09
1 IE-OS
1 8E-08
25E-10
Noncancer
Adult
Dose
(mg/kg-d)
1 IE 09
89E-10
1 IE 09
89E-10
2 OE 08
1 1E 09
1 1E^>9
23E-12
23E 12
77E 09
23E-12
54E 09
89E-10
1 IE 09
89E-10
B9E-10
1 9E 08
36E 09
23E 12
89E 10
89E-10
83E 09
1 IE 09
99E08
53E08
89E-10
49E-12
20E09
20E-09
30E09
40E 08
89E 10
89E 10
1 OE-08
4 OE 08
8 1E 08
89E-10
Noncancer
Child
Dose
(mg/kg-d)
40E 09
3 3E 09
40E09
33E09
73E08
40E09
40E-09
BSE 12
85E 12
2 9E-08
85E-12
2 OE 08
33E-09
40E-09
33E 09
33E-09
69E 08
1 4E-08
85E 12
33E 09
33E09
3 IE 08
4 IE 09
3 7E 07
20EO7
33E-09
1 BE 11
75E 09
75E09
1 1E 08
1 5E 07
33E09
33E 09
39E 08
1 5E 07
2 3E 07
33E 09
Noncancer
School age
Dose
(mg/kg-d)
24E09
20E09
24E09
20E-09
44E-08
24E09
24E09
51E-12
51E-12
1 7E 08
5 IE 12
1 2E08
2 OP 09
24E09
20E-09
20E 09
42E08
82E4»
51E-12
20E 09
20E49
1 9E 08
25E09
2 2E 07
1 2E07
20E^»
1 1E-11
46E 09
46E 09
6 BE 09
8 9E 08
20E 09
20E09
2 3E 08
89E 08
1 4E^)7
20E 09
Noncancar
Farmer
Dose
(mg/kg-d)
1 IE 09
89E 10
1 1E-09
89E-10
20EOB
1 1E 09
1 1E 09
23E 12
2 3E-12
77E-09
23E 12
54E-09
89E-10
1 IE 09
89E-10
89E-10
1 9E 08
36E 09
23E-12
89E-10
89E 10
83E^M
1 IE 09
99EOO
53E08
89E 10
49E-12
20EW
20E^»
30E^9
40E 08
B9E-10
89E 10
1 OE 08
40EOB
6 1E 08
89E 10
 3.7,8-TCDD
 2.3.7.8PCDD
 2.3.4.7.8^HxCDD
 2.36,78HxCDO
 I 3.7.8.9 HxCDD
 2.3.46.7.8 HpCDO
 :DD
 ).7,8 TCDF
 ? 3 7.8 PCDF
 3,4,7,8 PCDF
 .'.3 4 7 8-HxCDF
 ! 3 6 7 8-HxCDF
 j,4 6 7,8 HxCDF
1 5E+05
75E+04
1 5E+04
1 5E+04
1 5E*04
1 5E*03
1 5E»02
1 5E+04
75E*03
75E«04
1 5E»04
1 5E«04
1 5E«04
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
tiA
HA
NA
NA
NA
rjA
1 08E 11
678E 11
895E 11
1 66E 10
1 09E-10
1 24E 09
6 15E 09
8 77E 11
3 4SE 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Wl max
Wl max
Wl max
W1 max
W1 max
W1 max
Wl max
W1 max
W1 ma«
W1 max
W1 max
Wt max
W1 max
64E 12
40E 11
53E 11
98E 11
64E 11
73E 10
36E 09
52E 11
20E 10
2 BE 10
84E 10
79E 10
89E 10
22E 16
1 4E-15
1 9E 15
34E 15
2 3E 15
26E 14
1 3E 13
1 BE 15
7 2E 15
9 7E 15
30E 14
28E 14
3 IE 14
56E 16
35E 15
46E 15
86E 15
56E 15
64E 14
32E 13
45E 15
1 8E 14
2 4E 14
7 4E 14
69E 14
7 BF 14
34E-16
2 IE 15
2 BE 15
52E 15
34E 15
39E 14
1 9E 13
2 7E 15
1 IE 14
1 5E 14
45E 14
4 2E 14
4 7F 14
50E-16
3 IE 15
4 IE 15
76E 15
50E 15
57E 14
2 BE 13
40E 15
1 6E 14
22E 14
6GE 14
6?F 14
r, 9f 14
1 7E 15
1 IE 14
1 4E-14
2 7E 14
1 BE 14
20E 13
99E 13
1 4E 14
56E 14
7 5E 14
2 3E 13
2 ?F 13
7 <1F 13
65E 15
4 IE 14
54E 14
1 OE 13
66E-14
75E 13
3 7E 12
53E 14
2 IE 13
? BF 13
8 BF 13
8 IT 13
9 IF 13
39E 15
25E 14
33E 14
60E-14
40E-M
45E 13
22E 12
32E 14
1 3E 13
1 7E 13
52E 13
49E 13
«;•* 13
1 7E 15
1 IE 14
1 4E 14
27E 14
1 BE 14
20E 13
99E 13
1 4E 14
56E 14
75E 14
2 3E 13
2?f 13
2 4F 13
  ume V. Appendix V-14
-------
TABLE 22  Maximum li   -non Riski and fJoncancci HOs in Sub.nea Wl
CHEMICAL
Nitroaniline. 4
Nitrobenzene
Nitrophenol, 2-
Nilrophenof, 4
N NHroso-dl-n-butylamlne
N Nrboso-di-n-propytamlne
N-Nrtoosodiphenylamlne (Diphenylamme)
Nonachlorobiphenyt
Octachlorobiphenyl
Pentachlorobenzene
PentachloroWphenyl
Pentochlofonttrobenzene
Pentachlorophenol
Phenanthrene
Phenol
Pyrene
Safrole (5-(2-Propenyl) 1 .3 benzodloxole)
Styrene
Tetrachlorobiphenyl
Tetrachloroethane. 1,1,1,2
Tetrechloioethano, 1,1.2.2
Tetrachloroethene
Tetrachlorophenol, 2.3.4.6-
Tolueoe
Trtchloro-1.2.2-bif1uoroethane. 1.1.2-
Tricnkxobenzena, 1.2.4-
Trichkxoblphanyl
Trichknoethane. 1,1.1- (Methyl chloroform)
Trichtotoettiane. 1,1.2-
Trichlorot there
Tricblorofluoromelhane
Trlchlorophenot, 2.4.5-
Trkhkxophenol. 2.4.6-
Wnyl acetate
\J\ny\ chloride
Xylene, m/p- (m/p Dimethyl benzene)
Xylene, o- (o-Dim«thyt benzene)
2.3.7,8TCDO
1.2.3.7.8 PCDD
t .2 3.4 7 8 HxCDD
1.2, 3.6,7.8 HxCDD
1.2. 3 7. 8 9 HxCDD
1. 2,3,4 6.7,8-HpCDD
OCOO
2.3.7.BTCDF
1,2.3, 7.8 PCDF
2.3.4.7.8 PCDF
1 2,3 4.7.8 HxCDF
1.2,36.7.8-HxCDF
2,3.4,6. 7.8-HxCDF
Inhalation
Slope
Factor
(mg/Vg d)*-1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
20E01
20E-03
NA
NA
NA
NA
NA
NA
5 7E-02
60E-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E»05
75E+04
5E*04
5E»04
5E»04
5E«03
5E+02
1 5E*04
75E+03
75E*04
1 5E+04
1 5E*04
1 5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
0 02625
NA
000875
0 02625
0 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RID
(mg/kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E-O4
7 5E-03
NA
1 5E 01
75E453
NF
7 IE 02
NA
75E-03
NA
2 5E 03
7 5E-03
29E-02
2 1E«00
1 4E 02
NA
7 IE 02
1 OE-03
NA
50E02
25E-02
NA
1 4E 02
NA
50E 01
50E 01
NA
NA
NA
NA
NA
NA
NA
NA
tlA
NA
MA
NA
NA
Emission
Rale
(g/sec)
6 7E-06
55E06
67E 06
55E 06
1 2E-04
67E 06
67E-06
1 4E4I8
1 4E-08
4 BE -05
1 4E-08
3 4E-05
55E06
6 7E-06
55E-06
55E-06
1 2E 04
2 3E-05
1 4E-08
55E-06
5 5EX)6
SIE^K
68E 06
6 1E-04
33E 04
55E-O6
30E-08
1 3EO5
1 3E-05
19E05
2 5E-O4
55E-06
55E-06
64E-05
25E 04
3 BE 04
55E-06
1 08E-11
678E 11
895E-1I
1 66E 10
1 09E 10
1 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
Wt max
Wl max
Wl max
W1 max
Wl max
W1 max
Wl max
Wl max
Wt max
Wl max
Wl max
Wl max
W1 max
Wl max
W1 max
Wt max
W1 max
Wl max
Wl max
Wl max
Wl max
Wl max
Wt max
Wl max
Wl max
W1 max
Wl max
Wl max
W1 max
W1 max
Wl max
Wl max
W1 max
Wl max
Wt max
Wl max
Wl max
Wl max
W1 max
Wl ma
Wl ma
Wl ma
Wl ma
Wl ma
Wl ma
Wl ma
Wl ma
Wl ma
W1 ma
Wl ma
Adult
Cancer
Risk
NT
NT
NT
NT
1 4E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E-12
23E-11
22E-12
NT
NT
NT
NT
NT
NT
15E-11
23E-12
NT
NT
1 1E-12
NT
1 5E-09
NT
NT
34E 11
1 1E-10
28E 11
52E 11
34E 11
39E 1 1
1 9E 11
2 7E 11
54E 11
73E 10
44E 10
4 2E 10
4 7E 10
Child
Cancer
Risk
NT
NT
NT
NT
3 4E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
74E-12
58E-11
54E-12
NT
NT
NT
NT
NT
NT
37E-11
57E-12
NT
NT
28E-12
NT
3 BE -09
NT
NT
B4E-11
26E 10
69E 11
1 3E 10
85E 11
96E 11
48E 11
6 BE 11
3E 10
BE 09
IE 09
OE 09
2E 09
School-age
Cancer
Risk
NT
NT
NT
NT
20E 08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
45E-12
35E-11
33E-12
NT
NT
NT
NT
NT
NT
22E-11
35E-12
NT
NT
1 7E-12
NT
23E-09
NT
NT
51E-11
1 6E 10
4 2E-11
78E 11
5 1E-11
5 BE 11
29E It
4 IE 11
8 IE 11
1 IE 09
6 7E 10
63E 10
7 1E 10
Faimer
Cancer
Risk
NT
NT
NT
NT
30E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
66E-12
52E 11
4BE-12
NT
NT
NT
NT
NT
NT
33E 11
51E-12
NT
NT
25E-12
NT
34E-09
NT
NT
75E 11
23E 10
62E-11
1 1E-10
75E 11
66E 11
4 3E II
6 1E 11
1 2E 10
1 6E 09
99E 10
92E 10
1 OF 09
                                                                                                                                              Adult      Child   School-age   Faimer
                                                                                                                                            Noncancer Noncancer Noncancer Noncaneer
                                                                                                                                               HQ       HO        HQ        HQ
NT
62E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
73E-06
1 2E-07
NT
59E-09
1 2E-07
NT
5 1E-08
NT
1 2E-07
NT
33E-06
15E-07
35E^)6
2 5E 08
62E-08
NT
2 BE 08
20E-06
NT
79E07
36E-08
NT
73E-07
NT
12E-07
1 BE -09
NT
NT
NT
NT
NT
NT
NT
III
NT
NT
NT
rn
N1
NT
2 3E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
27E^»
44E-07
NT
22E48
44E-07
NT
1 9E-07
NT
44E-07
NT
1 2E-05
55E07
13E05
93E08
23E-07
NT
1 1E-07
75E^)6
NT
30EO6
1 3E07
NT
27E-06
NT
46E07
66E09
NT
NT
NT
NT
NT
NT
fH
til
NT
III
NT
HI
III
NT
1 4E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E-05
27E-07
NT
1 3E 08
2 7E-07
NT
1 1E-07
NT
27E-07
NT
75E 06
33E07
78E-06
5 6E 08
1 4E-07
NT
64E 08
46E06
NT
18E06
80E-08
NT
1 6E 06
NT
28E 07
40E 09
NT
NT
NT
HI
NT
til
NT
NT
NT
NT
ru
NT
in
NT
62E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
73E 06
1 2E-07
NT
59E 09
1 2E-07
NT
5 1E-08
NT
1 2E 07
NT
33E06
1 5E 07
35E 06
25E 08
62E 08
NT
2 BE 08
20E-06
NT
79E07
36F.08
NT
7 3E 07
NT
1 2E07
1 8E 09
NT
NT
NT
NT
NT
NT
fJT
NT
HI
III
W
NT
IJT
Volume V. Appendix V 14
-------
TABIC 22  Maximum Inhalation
                                and Noncancoi HQs in Subaina W1
CHEMICAL
1. 2.3.7.8.9 HxC OF
1.2.3 4.6. 7.8 HpCDF
1,2.3.4. 7.8 ,9-HpCDF
OCDF
Dloxin TEQ
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Coppw
lead
Mercury (an 4 MeHg)
•Jickel
selenium
Silver
thallium
!lne
lydrogen chloride
otal nitrogen oxides (NOx)
otal sulfur oxides (SOx)
'articulate matter
tespirable particulars
Inhalation
Slope
Factor
(mg/kg -d)'-1
1 5E«04
1 5E*03
1 5E«03
1 5E+02

NA
NA
SO
NA
84
61
41
NA
NA
NA
NA
064
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0 004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE 04
75E-05
36E 05
1 3E 03
1 3E 04
1 3E 03
25E-01
NA
NA
2 1E 05
50E 03
1 3E 03
1 3E 03
1 BE OS
7 5E -02
50E 04
NA
NA
NA
NF
Emission
Rate
(9/sec)
293E 10
930E09
t 22E-09
1 89E 08
428E08
24E-04
42E-06
37E-05
1 SE^M
33E-08
16E4«
71E^>7
7 1E«7
94E05
43E^5
1 4E 03
50E4)6
4 7E«4
1 5E05
34E05
1 2E 04
32E^)2
24E»00
91E 02
7 2E 02
72E-02
Subaiea
Wl max
Wl max
W1 max
Wl max

Wl max
Wl max
Wt max
Wt max
Wl max
Wl max
W1 max
Wl max
Wl max
Wl max
Wt max
Wl max
Wl max
Wl max
Wl max
W1 max
Wl max
Wl max
Wl max
Wl max
Wt max
Off site
Vapor
Cone
(ug/m3)
1 7E 10
55E 09
72E-10
1 1E-08

1 4E-04
25E-06
22E-05
89E 05
1 9E 08
94E-06
4 2E-07
42E 07
55E 05
2 5E 05
8 3E-04
30E-06
2 8E 04
89E 06
20E 05
7 IE -05
1 9E 02
1 4E«00
54E 02
4 2E 02
4 2E 02
Cancer
Adult
Dose
(mg/kg-d)
6 1E 15
1 9E 13
25E 14
39E 13
89E 13
50E-09
87E 11
77E-10
3 IE 09
69E 13
33E-10
15E-11
15E 11
20E-09
89E-10
29E-08
1 OE 10
98E-09
3 IE 10
7 IE 10
25E09
6 6E-07
50E-05
19E^>6
1 5E 06
15E-06
Cancer
Child
Dose
(mg/kg d)
1 5E-14
48E-13
63E 14
98E-13
22E 12
1 2E-08
22E-10
19E 09
7 BE 09
1 7E 12
83E-10
37E-11
37E-11
4 9E 09
22E 09
72E 08
26E-10
2 4E 08
78E 10
1 BE 09
62E09
1 7E^)6
1 3E 04
47E-06
37E 06
37E 06
Cancer
School age
Dose
(mg/kg-d)
92E-15
29E-13
38E 14
59E 13
1 3E-12
75E-09
1 3E-10
1 2E-09
47E-09
10E 12
50E-10
22E-11
22E-11
29E^)9
1 3E 09
4 4E 08
1 6E-10
1 5E 08
4 7E 10
1 1E 09
38E=09
10E-06
7 6E 05
2 BE 06
23E06
23E06
Cancer
Farmer
Dose
(mg/kg d)
1 4E-14
43E 13
56E 14
8 7E-13
20E-12
1 1E^8
I9E 10
1 7E 09
69E-09
15E-12
74E-10
33E-11
33E-11
43E-09
20E09
6 5E 08
23E-10
2 2E 08
69E 10
16Efl9
55E09
1 5E-06
1 1E4J4
42E-08
33E06
33E-06
Noncancer
Adult
Dose
(mg/kg d)
4 7E 14
1 5E 12
20E 13
31E 12
69E 12
39E-08
68E-10
60E 09
24E^)8
53E 12
26E-09
1 1E-10
1 1E 10
t 5E 08
69E 09
2 3E 07
8 IE 10
76E08
24E09
55E^»
19E08
52E^)6
39E04
1 5E-05
t 2E 05
1 2E-05
Noncancer
Child
Dose
(mg/kg d)
1 BE 13
56E 12
74E 13
1 IE 11
26E 11
1 4E 07
25E 09
2 2E 08
9 IE 08
20E-11
97E09
43E-10
43E-10
5 7E-08
26E-08
8 5E 07
30E-09
28E07
9 IE 09
2 IE 08
7 2E 08
19E05
1 5E 03
55E 05
43E05
43E 05
Noncancer
School age
Dose
(mg/kg d)
1 IE 13
34E 12
45E 13
69E 12
1 6E 11
B8E 08
15E-09
1 3E-08
5 5E 08
1 2E 11
5 BE 09
26E-10
26E-10
3 4E 08
1 6E 08
51E07
18E-09
1 7E 07
55E4W
12E06
44E08
1 2E 05
8 BE 04
33E 05
26E 05
26E-05
Noncancer
Farmer
Dose
(mg/kg d)
4 7E 14
1 5E-12
20E 13
31E-12
69E-12
39E-08
6BE-10
60E 09
2 4E 08
53E 12
26E-O9
1 1E-10
1 IE 10
1 5E 08
69E09
23E^)7
8 IE 10
76E4)8
24EXN
55E09
1 9E 08
52E-06
39E 04
1 5E^)5
1 2E 05
1 2E-05
 IOTES
  NA - Not applicable
  NF • Not found
  NT - No loxicity information
  HO • Hazard quotient    ;
  HI • Hazard index
  lume V Appends V 14
-------
                  V    )
FABLE 22  Maximum Inhalation Risks and Noncancer HQs in Suhaina W1
CHEMICAL
123.78 9 HxCDF
1. 2.3.4,6.7.8 HpCDF
1, 2,3.4, 7.8.9-HpCDF
OCDF
Dioxin TEQ
Aluminum
Antimony
Arsanlc
Barium
Beryllium
Cadmium
Chromium (hexavalent)
Chromium (bivalent)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
rhalllum
Zint
Hydrogen chloride
Total nitrogen oxides (NOx)
Total sulfur oxides (SOx)
Particulat* matter
Resplrable particulates
Inhalation
Slope
Factor
(mg/kg-d)A-1
1 5E+04
1 5E*03
1 5E»03
1 5E*02

NA
MA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg-d)
NA
NA
NA
NA

NA
1 OE-04
75E-05
36E-05
1 3E-03
1 3E-04
1 3E-03
25E-01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E 03
1 8E-05
75E-C2
50E-O4
NA
NA
NA
NF
Emission
Rate
(g/sec)
293E-10
9 30E 09
1 22E 09
1 89E 08
4 28E 08
24E 04
42E46
37E-05
1 5E-04
33E-08
16E-05
71EXJ7
7 1E 07
94E4K
43E^»
1 4E-03
50E 06
47E^>4
1 SE^fi
34E05
1 2E-04
32E-02
24E«00
9 1E^)2
7 2E 02
72E-02
Subarea
W1 max
W1 max
W1 max
W1 max

W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
W1 max
Adult
Cancer
Risk
9 1E-11
29E-10
38E-11
59E 11
29E09
NT
NT
3 BE -08
NT
58E-12
20E-09
60E-10
NT
NT
NT
NT
87E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
23E 10
72E 10
95E 11
1 5E 10
7 3E-09
NT
NT
9 6E-08
NT
1 4E 11
5 IE 09
15E-09
NT
NT
NT
NT
22E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
1 4E 10
44E 10
57E 11
89E 11
44E-09
NT
NT
5 8E 08
NT
87E 12
3 IE 09
91E-10
NT
NT
NT
NT
1 3E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmet
Cancer
Risk
20E 10
64E 10
85E-11
1 3E 10
65E-09
NT
NT
8 SE 08
NT
1 3E-11
45E-09
13E-09
NT
NT
NT
NT
1 9E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                             Adult      Child   School age   Farmer
                                                                                                                                           Noncancer  Noncancer Noncancer  Noncancer
                                                                                                                                              HQ        HQ        MQ        HQ
NT
NT
NT
NT
NT
NT
6 BE -08
80E-05
6 8E-04
43E-09
21E-05
92E-08
46E-10
NT
NT
1 1E-02
1 6E 07
8 IE 05
19E06
3 IE 04
2 6E 07
1 OE-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E4*
30E4J4
2 5E 03
16E-08
77E^)5
34E47
1 7E-09
NT
NT
39E-02
60E07
23E-04
72E^)6
1 2E-03
97E^)7
39E^)2
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E-05
1 BE 04
1 5E 03
96E-09
47E-05
2 1E-07
10E-09
NT
NT
2 4E 02
36E07
14E 04
44E06
7 IE 04
5 BE 07
23E 02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 BE 06
80E 05
6 BE 04
43E-09
2 1E-05
92E 08
46E-10
NT
NT
1 IE 02
1 6E 07
6 IE 05
1 9E 06
3 IE 04
2 6E 07
1 OE 02
NT
NT
NT
NT
                                                                               Total Risk   6 5E-08    1 6E-07    9 8E-08    1 4E-07
                                                                                                                                   Total HI    25E02    9 3E 02   5 6E 02    2 5E 02
MOTES.
  NA - Not applicable   v
  NF • Not found
  NT • No foxicHy information
  HQ * Hazard quotient
  HI - Hazard index
 /olume V. Appendix V-14
-------
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HEMICA
Inh
F
(mg/
                                                                                                                                                           en 7
                        TT ft  i. b
                       0 2.-S sr
                       33^5
RAC
(mg/m
Inhalati
RfD
(mg/kg
Emission
Rate
(g/s«c)
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Dose
(mg/kg
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-------
                  /"" \
ABLE 23  Maximum IK,    /on Risks and Noncancer HQs in Sub.iira W2
;HEMICAL
Vcenaphthena
Vcenaphthylane
kceUldehyde
\cetont
^catophanon*
Kcrylonttrile
knthracene
lenzan*
tonzolc acid
lanzotrtchlofida
lenio(a)anthracene
»erxzo{a)pyr»ne
)anzo(b)fluorinlhana
)anzo(p,h ,1) parylana
lemo(k)fluoranlh«ne
)ls(2-chloro«thoxy) m«ttiane
tis(2-chloro«thyl)ether
lls(2-chloroljopropyl)ether
)ls(2-«thylhexyl)phthalate
Iromodichloromethane
Iromoform
Iromomethane
Itomodiphenyl ether, p-
lutanona, 2- (Methyl ethyl ketone)
lulylbenzylphthalata
Carbon disulfide
:arbon tabachlorida
;hlordene
;hloro-3-m«thylphanol. 4-
;hloroaniline. p- (4-Chloroanilme)
;hlotob«nzene
;htotobanzilata
:hloroethane (Ethyl chloride)
Chloroform
;hloromethane
:hloronaphthalene. b«ta
:hloiophenol. 2-
;hlorodiphanyl ather, 4- -:
;hrysen«
:resol. m-
:r»sol. o- (2-Ma«hyOE. 4,4'-
)ibenz(a.h)anthracene
Jibromochloromethane
)ichlorob«nzena. 1 3-
>ichlorob«fuene. 1.4-
)ichlorob«r\iene. 1.2-
hchlorobervzidme. 3.3'
)ichlorobiphenyt
Inhalation
Slope
Factor
(mg/kg-d)*-1
NA
NF
7 7EO3
NA
NA
24E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E»00
NA
NA
NA
39E^)3
NA
NA
NA
NA
NA
53E-02
1 3E»00
NF
NA
NA
2 7E-01
NA
8 1E^>2
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
fJA
NA
RAG
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
004375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
HA
NA
Inhalation
RfD
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
25E 02
1 4E 04
7 5E 02
43E04
1 OE»00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
5 OE 03
50E 03
50E 03
36E-04
NA
7 1E 02
50E 02
7 1E-04
1 4E 04
1 5E-05
NF
1 OE-03
1 4E 03
5 OE-03
7 1E-01
2 5E-03
NA
20E 02
1 3E-03
NF
NA
1 3E 02
1 3E 02
1 3E 03
NA
64E 04
NA
NA
50E 03
NA
5 7E 02
1 <1E 02
NA
NA
Emission
Rat*
(g/sec)
67E^>6
67E 06
30E 04
2 9E 03
29E434
20E4J4
55E^>6
1 5E^)5
1 1E-05
32E-05
55E06
55E^)6
S5E-06
55E06
55E4»
6 7E 06
1 3E 05
87E-06
3 7E-05
1 OE 04
55E 06
49E^)4
8 7E^)6
5 IE 05
55E^»
89E^)5
16E^)4
55E-07
67E06
67E4W
55E-06
37E 05
49E 04
2 7E-04
25E 04
67E 06
55E 06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
556 07
55E 06
2 6E 05
55E 06
55E 06
S5E 06
33E 05
4 7E 08
Subarea
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2m»x
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2max
W2 max
W2 max
W2 max
W2max
W2 max
W2 ma«
W2 ma»
VV2 mat
W2 mai
W2 ma.
W2 ma.
W2 ma<
W2 ma.
W2 ma.
W? ma.
Adult
Cancer
Risk
NT
NT
1 7E 11
NT
NT
36E-10
NT
32E 12
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-10
NT
NT
NT
1 6E-13
NT
NT
NT
NT
NT
6 IE 11
53E-12
NT
NT
NT
74E-11
NT
1 6E 10
t 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
W
NT
tIT
NT
NT
m
UT
NT
NT
Child
Cancer
Risk
NT
NT
43E-11
NT
NT
89E-10
NT
79E-12
NT
NT
NT
NT
NT
NT
NT
NT
2 7E-10
NT
NT
NT
39E 13
NT
NT
NT
NT
NT
1 5E 10
1 3E-11
NT
NT
NT
1 9E 10
NT
39E-10
28E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
tIT
m
NT
NT
in
in
fii
School age
Cancer
Risk
NT
NT
26E-11
NT
NT
54E-10
NT
48E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-10
NT
NT
NT
24E 13
NT
NT
NT
NT
NT
93E-11
79E 12
NT
NT
NT
1 1E-10
NT
24E 10
t 7E-H
NT
NT
NT
NT
NT
NT
NT
m
NT
m
HI
fJT
HI
m
III
(II
tIT
Farmer
Cancer
Risk
NT
NT
38E-11
NT
NT
79E-10
NT
70E-12
NT
NT
NT
NT
NT
NT
NT
NT
24E-10
NT
NT
NT
35E-13
NT
NT
NT
NT
NT
1 4E 10
1 2E-11
NT
NT
NT
1 7E 10
NT
35E-10
25E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
fJT
in
m
(IT
m
m
tn
NT
                                                                                                                                           Adult      Child   School age   Farmer
                                                                                                                                         Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                            HO        HQ       HQ       HQ
26E-08
NT
2 7E-05
67E-06
6 7E-07
81E05
42E09
20E4J6
65E-10
NT
NT
NT
NT
NT
NT
NT
NT
3 BE 08
43E-07
1 2E^6
63E^»
79E-05
NT
41E-08
63E-09
72E^)6
64E^»
2 1E^)6
NT
38E^)7
22E07
42E07
39E08
61E-06
NT
1 9E^>8
25E-07
NT
NT
25E08
25E08
25E-07
NT
49E 07
NT
NT
30E-07
UT
55E 09
? 2F Of)
Ml
III
9 6E-08
NT
1 OE 04
25E05
25E 06
30E 04
1 6E 08
74E06
24E-09
NT
NT
NT
NT
NT
NT
NT
NT
1 4E^)7
16E-06
44E06
24E07
29E-04
NT
1 5E 07
2 4E 08
2 7E05
2 4E 04
79E 06
NT
1 4E06
83E07
16E06
1 5E 07
23E05
NT
72E 08
95E 07
NT
NT
95E 08
95E 08
95E 07
NT
1 BF. 06
NT
HI
1 IF 06
HI
2 IT 08
8 If 08
III
in
5 BE 08
NT
6 IE 05
1 5E 05
1 5E 06
1 BE 04
95E09
45E06
15E09
NT
NT
NT
NT
NT
NT
NT
NT
8 7E 08
9 7E 07
27E06
1 4E 07
1 BE -04
NT
94E 08
1 4E 08
16E05
1 4E 04
4 BE 06
NT
87E 07
50E 07
96E 07
8 9E 08
1 4E-05
NT
43E 08
57E 07
NT
NT
57E 08
5 7E 08
57F 07
NT
1 IE 06
NT
NT
68F 07
NT
1 2F. OB
5 OF 08
tit
NT
2 6E-08
NT
27E05
67E 06
6 7E 07
8 IE 05
42E 09
20E 06
65E-10
NT
NT
NT
NT
NT
NT
NT
NT
3 BE 08
43E 07
1 2E 06
63E08
79E05
NT
4 IE 08
63E09
72E T6
64E 05
2 IE 06
NT
3 BE 07
22E 07
42E 07
39E08
6 1E 06
NT
1 9E 08
25E 07
NT
NT
25E 08
25E 08
25E 07
NT
4 9E 07
NT
tn
3 or 07
in
55F 09
2 ?F 08
NT
in
olume V. Appendix V 14
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   VBLE 23 Maximum Inhalation Risks and Noncancec HOs m Subaipa W2
HEMICAL
Ichlorodrfluoromethana
ichloioetrtan*. 1,1- (Ethylidene dichloride)
i ichloroethane. 12
Ichloroethene, 1,1- (Vlnylidine chloride)
ichloroettiene (trans), 1,2-
ichlorophenol, 2.4
ichloropropane. 1.2- (Propylene dichloride)
Ichloropropane (els), 1,3-
ichloropropene (trans), 1.3-
'imethoxyberaidlne. 3.3'-
iim*thy(ph«nol. 2.4-
ilrrwthyl phthalate
(i-n butylphthalale
'lnltrotolu«n«. 2.6-
'lnltro-2-rnethylphenol, 4.6-
llnltfophenol. 2.4-
Unttrotoluen*. 2,4-
Hoxane, 1.4-
'l(n)octyt phthalate
'. 2.4-
thyt methacrylate
thyioenzene
thylene dibromlde
thylene oxid*
thylene thioutea
luoranthene
luorene
ormaldehyde
unVral
toptechfof
teptachloroblphenyl
texachlorobenzene
lexachlorob'phenyl
lexachlorobutadiene
lexachknocyclohexan*. gamma (Llndane)
lexachlorocyclopentadien*:
lexachloroethane
Texachlorophene
taxanone, 2-
ndeno(1 .2 3-cd)pytene
sophoron*
^aleic hydiuide
^ethoxychlor
Methyl t butyl ether
Methyl 2 Pentanone, 4 (MIBK)
idethylene chloride
detnylnaphthalene. 2
tfonocnlorobiphenyl
'•laohthalene
'(itroamline 2-
"Mioaniline 3-
Inhalalion
Slope
Factor
(mg/kg-d)'-
NA
NA
9 IE -02
1 2E+00
NA
NA
NA
13E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E+00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
t 6E-03
NF
NA
NA
NA
NF
RAG
(mg/m3)
005
0125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
COOOO5
NA
000007
0035
0035
0175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
000005
(if
Inhalation
R(D
(mg/kg-d)
1 4E 02
NA
2 3E 03
50E-03
75E-04
29E-04
1 4E4J3
1 4E-03
20E-01
NA
50E-03
NA
25E-02
25E-04
NF
50E04
50E-04
NA
50E 03
2 5E-03
2 3E 02
7 1E-02
1 4E-O5
NA
20E 05
1 OE^)2
1 OE-02
50E-02
36E-03
1 3E-04
NA
20E-04
NA
50E-05
75E-05
50E-06
25E04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 IE 01
5 7E 03
2 1E 01
NF
NA
1 OE 02
1 4E 05
NF
Emission
Rate
(g'sec)
25E-04
3E-05
3E 05
3E-05
3E05
55E-08
3E-05
3E-05
3E-05
7E-05
2E-04
55E-08
5 SEW
16E-05
55E-08
55E-06
55E-06
49E04
55E-06
39E-05
25E4M
50E04
1 2E-04
3 IE-OS
1 5E-10
55E 06
67E-06
61E-04
55E-06
55E-07
1 4E-08
55E-06
1 4E 08
10E-04
55E05
55E-06
55E 06
32E 05
64E 05
55E 06
6 7E-06
1 2E 04
55E 07
3E 05
3E 05
OE 04
2E 05
7E 08
55E 06
6 7E 06
6 7E 06
Subarea
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2mej<
W2max
W2max
W2max
W2max
W2m«x
W2max
W2max
W2m«x
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2ma»
W2 max
W2 max
W2max
W2 max
W2 max
W2max
W2max
W2 max
W2 max
Adult
Cancer
Risk
NT
NT
84E 12
1 1E-10
NT
NT
NT
1 2E-11
1 2E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
65E-10
79E-11
NT
NT
NT
20E-10
NT
1 8E-11
NT
65E-11
NT
58E-11
NT
NT
57E-13
NT
NT
NT
NT
NT
NT

nr
48E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
2 1E-11
28E-10
NT
NT
NT
30E-11
30E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E-09
20E-10
NT
NT
NT
50E-10
NT
46E-11
NT
1 6E-10
NT
1 5E-10
NT
NT
1 4E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 11
fJT
UT
NT
NT
NT
School-age
Cancer
Risk
NT
NT
1 3E-11
1 7E-10
NT
NT
NT
1 8E-11
1 8E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
97E-10
1 2E-10
NT
NT
NT
30E-10
NT
28E-11
NT
99E-11
NT
88E-11
NT
NT
86E-13
NT
NT
NT
NT
NT
NT
NT
NT
7 3F. 12
N T
UT
NT
NT
NT
Farmer
Cancer
Risk
NT
NT
19E-M
25E-10
NT
i^( i
NT
NT
27E-11
2 7E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
t 4E-09
1 BE-10
NT
NT
NT
4SE-10
NT
4 1E-11
NT
1 5E-10
NT
M 1
1 3E-10
NT
NT
1 3E-12
NT
NT
I » I
NT
NT
NT
NT

NT
1 1 F 1 1

NT
NT
Nf
NT
                                                                                                                                              Adult      Child   School-age  Farmer
                                                                                                                                            Noncancer  Noncancer Noncancer Noncancer
                                                                                                                                               HO       HO        HQ        HO
9 9E 07
20E-08
NT
3 2E 07
1 4E-07
4 2E 07
25E-06
50E-07
50E-07
4 BE -09
NT
63E-08
NT
36E-08
1 3E-06
NT
63E-07
63E-07
NT
63E-08
8 9E-07
63E^)7
40E-07
46E-04
NT
42E 10
32E08
3 BE -08
70E-07
B9E 08
25E-07
NT
16E-09
NT
1 2E44
42E05
63E05
13E^>6
25E-05
NT
NT
77E09
53E08
2 5E 08
34E 09
1 3E 07
1 1E 07
HI
NT
32E 08
? 7r n-;
m
3 7E 06
7SE.-08
NT
1 2E 06
5 4E 07
16E06
94E06
1 9E 06
1 9E 06
1 8E-08
NT
24E-07
NT
1 3E 07
47E-06
NT
24E-06
24E-06
NT
24E-07
33E^)6
23E-06
15E^)6
1 7EX)3
NT
16E09
1 2E^)7
1 4E^)7
26E 06
33E-07
95E-07
NT
S9E-06
NT
43E-04
1 6E 04
2 4E 04
47E 06
92E 05
NT
NT
29E 08
20E 07
95E 08
1 IF 08
4 !f 07
4 OF 07
NT
m
1 2F 07
t Of 04
m
22E 06
4 5E-08
NT
7 2E 07
3 2E 07
95E 07
57E06
1 IE 06
1 IE 06
1 1E-08
NT
1 4E-07
NT
8 IE 08
29E-06
NT
14E06
1 4E-08
NT
1 4E 07
20E-06
14E06
9 IE 07
1 OE-03
NT
95E 10
71E4W
8 7E-OB
16E06
20E07
5 7E-07
NT
36E-06
NT
26E04
95E 05
1 4E 04
29E 06
55E 05
NT
NT
1 7E08
1 2E 07
57E 08
76E 09
28F 07
24F 07
m
NT
7 IE 08
fi IF 05
NT
9 9E 07
2 OE-08
NT
3 2E 07
1 4E 07
4 2E 07
25E06
50E4)7
50E07
48E-09
NT
63E-08
NT
36E08
1 3E-06
NT
63E^)7
63E-07
NT
63E^)8
89E07
8 3E 07
40E-07
46E-04
NT
42E 10
32E 08
3 BE 08
70E4)7
89E 08
25E^)7
NT
1 6E -06
NT
1 2E 04
42E 05
63E 05
13E06
25E-05
NT
NT
7 7EO9
53E 08
25E 08
34E 09
1 3E 07
1 IF 07
NT
ru
32E 08
? ?F 05
NT
/olume V, Appendix V-14
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                                                                                                             t- t6 I*: r^ a> 7 o «b f-' >~ >-
                                                                                                             «q r-| V ID F~' V Q CO r^ r*' v ID ID
-------
TABLE 23  Maximum \
/(ion Risks and Noncancer HQs in Subaipa W2
CHEMICAL
Nitroaniline, 4-
Nitrobenzene
Mrtrophenol. 2-
^itrophenol, 4-
N-Nrtroso-di-n-butylamlne
'1 Nrboso-di-n-propylamine
"J -NHrosodlphenytamlne (Diphenylamine)
•Jonachloroblphenyl
Octachlofobiphenyi
°errt«chlofoberwene
PentachloroWphenyl
Pentachloronrtrobanzene
3entochlorophenol
3henanthrene
3henol
>ytene
Safrole (5-(2-Propenyl)- 1 ,3-benzodioxole)
Styrene
fetrachlorobiphenyl
letiachloroethane, 1,1,1,2-
letrachloroettiane, 1.1.2,2-
fetiachloroethene
fettachlorophenol, 2.3.4,6-
loluene
lrtchlo«o-1.2,2-trrnuoroethane, 1.1.2-
rrichlotobenzene, 1.2.4-
CrlcMorobiphenyt
Trlchlofoethane, 1,1.1- (Methyl chloroform)
Frichloroethane, 1.1,2-
frlchloroelhene
Trichlofofluoromethane
rrichlorophenol. 2.4.5-
rrichtorophenol, 2,4,6-
f\ny\ acetate
/Inyl chloride
(ylene. m/p- (m/p-Dlmethyl benzene)
(ylene. o- (o-Dlmethyl benzene)
!.3.7,8-TCDO
l. 2,3.7,8 PCDD
2.34.7.8-HxCDD
1 236,78-HxCDD
1.2 3.7.B.9HxCDO
1,2,3,4.6.7.8-HpCDD
X;DD
'.3.7.8 TCDF
1.2.3.7,8 PCDF
' 34 7.8 PCDF
1.2,3. 4. 7 8 HxCDF
! 2 36.7.8 HxCDF
'.3.4.6.7 8 HxCDF
Inhalation
Slope
Factor
(mg/kg d)*-1
NF
NA
NF
NF
54E*00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
2 OE 01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
60E-03
NA
NA
1 OE-02
NA
30E-01
NA
NA
1 5E+05
75E+04
1 5E*04
1 5E*04
1 5E»04
1 5E+03
1 5E+02
1 5E+04
75E«03
75E»04
1 5E»04
1 5E»04
1 5E«04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
002625
NA
000875
002625
0 1
7 5
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
fJA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/Vg d)
NF
1 4E 04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E 04
7 5E-03
NA
1 5E 01
75E-03
NF
7 1E 02
NA
7 5E-03
NA
25E 03
75E 03
29E 02
2 1E«00
1 4E-02
NA
7 1E-02
1 OE-03
NA
5 OE-02
25E 02
NA
1 4E-02
NA
50E 01
50E 01
NA
NA
NA
NA
NA
flA
NA
NA
NA
NA
NA
flA
NA
Emission
Rate
(g/sec)
6 7E 06
55E 06
6 7E 06
55E 06
1 2E 04
67E 06
6 7E-06
1 4E 08
1 4E 08
4 BE -05
1 4E 08
34E 05
55E-06
6 7E-06
55E06
5 5E-06
1 2E-04
23E 05
1 4E-08
55EO6
55E-06
5 1E-05
6 BE 06
61E-04
3 3E-04
55E 06
30E-08
1 3E 05
1 3E^)5
1 9E-05
25E 04
55E 06
55E-06
64E-05
25E 04
3 BE -04
55E-06
108E-M
6 78E 11
895E 11
1 66E 10
1 09E 10
1 24E 09
6 15E 09
877E 11
3 45E 10
467E 10
1 43E 09
1 33E 09
1 50E 09
Subarea
W2max
W2max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2m»x
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2 max
W2 max
W2 ma«
W2 max
W2 max
W2 ma«
W2 max
W2 ma«
W2 ma«
W2 mai
AduH
Cancer
Risk
NT
NT
NT
NT
4 BE 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-12
83E-12
7 7E-13
NT
NT
NT
NT
NT
NT
53E-12
82E-13
NT
NT
4 1E-13
NT
54E-10
NT
NT
1 2E 11
3 BE 11
99E 12
1 BE 11
1 2E 11
1 4E 11
6 BE 12
9 7E 12
1 9E 11
26E 10
1 6E 10
1 5E 10
1 7E 10
Child
Cancer
Risk
NT
NT
NT
NT
1 2E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E-12
2 IE 11
1 9E-12
NT
NT
NT
NT
NT
NT
1 3E-11
20E-12
NT
NT
1 OE-12
NT
1 4E-09
NT
NT
30E-11
94E 11
25E-11
46E 11
30E 11
34E 11
1 7E 11
2 4E 11
4 BE 11
64E 10
39E 10
3 7E 10
4 2E 10
School age
Cancer
Risk
NT
NT
NT
NT
7 3E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-12
1 2E 11
1 2E-12
NT
NT
NT
NT
NT
NT
79E-12
1 2E-12
NT
NT
61E-13
NT
82E-10
NT
NT
1 8E-11
5 7E-11
1 5E-11
2 BE 11
1 BE 11
2 IE 11
1 OE 11
1 5E 11
2 9F 11
39E 10
24E 10
2 2E 10
2 <>£ 10
Farmer
Cancer
Risk
NT
NT
NT
NT
1 1E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
23E-12
1 8E-11
1 7E-12
NT
NT
NT
NT
NT
NT
1 2E-11
1 BE-12
NT
NT
90E-13
NT
1 2E-09
NT
NT
27E It
84E It
22E 11
4 1E 11
2 7E 11
3 IE-It
1 5E 11
2 2E 11
4 2E 11
5 BE 10
35F 10
33E 10
3 7E 10
                                                                                                                                              AduH      Child    School age  Farmer
                                                                                                                                            Noncancer Noncancer Noncancer Noncancer
                                                                                                                                               HQ       HQ       HQ        HQ
NT
2 2E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E-06
42E08
NT
2 1E-09
4 2E-08
NT
1 BE -08
NT
42E-08
NT
1 2E-06
5 2E-OB
12E06
89E 09
2 2E-08
NT
1 OE 08
7 2E-07
NT
2 BE -07
1 3E-08
NT
2 6E-07
NT
4 4E-08
63E-10
NT
NT
NT
NT
NT
NT
NT
NT
(IT
IIT
NT
NT
flT
NT
83E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
97E-06
1 6E-07
NT
79E-09
1 6E-07
NT
6 8E-08
NT
1 6E-07
NT
44E46
1 9E-07
46E06
3 3E-08
8 3E-OB
NT
3 BE 08
2 7E^)6
NT
1 IE 06
4 7E-08
NT
9 7E-07
NT
1 6E-07
24E 09
NT
NT
NT
NT
HI
HI
NT
til
fll
111
NT
Ml
Ml
NT
50E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 BE 06
95E-08
NT
4 BE 09
9 5E-08
NT
4 1E-08
NT
95E-08
NT
27E4W
1 2E 07
28E06
2 OE-08
50E06
NT
2 3E 08
1 6E-06
NT
6 4E 07
2 9E-08
NT
5 BE -07
NT
99E 08
1 4E 09
NT
NT
NT
NT
til
NT
III
N!
Ml
NT
fll
NT
HI
NT
22E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E 08
4 2E-OB
NT
2 IE 09
42E-08
NT
1 BE -08
NT
42E08
NT
1 2E-06
52E08
12E06
B9E09
22E08
Ni
1 OE 08
72E-07
NT
2 BE 07
1 3E-OB
NT
2 BE -07
NT
44EOB
83E-10
NT
NT
NT
NT
NT
NI
NT
NT
III
NT
NT
NT
NT
 'olume V. Appendix V-14
-------
TABLE 23  Maximum Inhalation Risks and Uoncancei HQs m Subaiea W2
CHEMICAL
1.2,3,7.8 9 HxCDF
1. 2,3.4,6.7.8 HpCDF
1.2.3.4.7.8.9 HpCDF
OCDF
Dloxln TEQ
Aluminum
Antimony
Ars«nlc
Barium
B«ryllium
Cadmium
Chromium (hexavalenl)
Chromium (trivalenl)
Copper
Lead
Mercury (and MeHg)
Nickel
Selenium
Silver
Thallium
Zinc
Hydrogen chloride
Total nitrogen oxides (NO1
Total sulfur oxides (SOx)
Pattculate matter
Resplrable particulates
Inhalation
Slope
Factor
(mg/kg-d)*- 1
1 5E»04
1 5E+03
1 5E«03
1 5E»02

NA
NA
50
NA
84
61
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
1 OE^>4
75E-05
3 6E 05
1 3E-03
1 3E-04
1 3E-03
25E-01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E 03
1 8EX)5
75E 02
50E^>4
NA
NA
NA
NF
Emission
Rat*
(g/sec)
293E 10
930E4I9
1 22E-09
1 89E^)8
4 28E^>8
24E44
42E06
37E^»
1 5E^)4
33E-08
16E-05
71E-07
7 1E47
94E4tt
43E^)5
1 4E-03
50E-06
4 7E-04
1 5E 05
34E-05
1 2E 04
3 2E-02
24E»00
9 1E 02
7 2E 02
7 2E 02
Subarea
W2max
W2 max
W2max
W2max

W2max
W2max
W2max
W2max
W2max
W2mw
W2 max
W2max
W2 max
W2max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
Ofl-sile
Vapor
Cone
(ug/m3)
62E-11
20E 09
26E 10
40E 09

50E 05
8 8E-07
78E-06
3 2E-05
69E 09
34E 06
1 5E 07
1 5E 07
20E 05
90E 06
29E 04
1 IE 06
99E 05
32E 06
7 1E-06
25E 05
67E 03
5 IE 01
1 9E 02
1 5E 02
1 5£ 02
Cancer
Adult
Dose
(mg/kg d)
2 2E 15
69E 14
90E 15
1 4E 13
32E 13
1 BE 09
3 IE 11
2 7E 10
1 1E-09
24E 13
12E 10
52E-12
52E 12
70E 10
32E 10
1 OE 08
37E-11
3 5E 09
1 IE 10
25E 10
89E 10
2 4E-07
1 8E 05
6 7E 07
53E 07
5 3E-07
Cancer
Child
Dose
(mg/kg-d)
54E 15
1 7E 13
22E 14
35E-13
79E 13
44E 09
77E 11
68E 10
28E09
6 IE 13
29E 10
1 3E-11
1 3E-11
1 7E 09
79E 10
2 6E 08
92E-11
87E09
28E 10
63E 10
22E 09
5 9E 07
45E05
1 7E 06
1 3E-06
1 3E 06
Cancer
School age
Dose
(mg/kg d)
33E-15
1 OE 13
1 4E 14
2 1E-13
4 BE- 13
27E-09
47E-11
41E-10
1 7E-09
37E-13
1 BE 10
79E12
79E-12
10E^»9
4 BE 10
1 6E48
56E 11
52E^9
1 7E 10
3 BE 10
1 3Efl9
36E^)7
27E^5
1 OE^6
80Efl7
80EXJ7
Cancer
Farmer
Dose
(mg/kg-d)
4 BE 15
1 5E-13
20E 14
31E 13
70E-13
39E 09
69E-11
61E-10
25E09
54E 13
26E 10
12E-11
1 2E 11
1 5E 09
7 IE 10
23E 08
82E 11
7 7E-09
25E 10
56E 10
20E09
53E07
40E 05
1 5E 06
1 2E 06
1 2E 06
Noncancer
Adult
Dose
(mg/kg d)
1 7E 14
54E 13
70E 14
1 1E 12
25E 12
1 4E-08
24E-10
21E-09
86E-09
19E 12
92E 10
41E-11
41E-11
54E-09
25E-09
8 IE 08
29E 10
27E08
86E-10
20E-09
69E09
1 8E06
1 4E 04
52E06
4 IE 06
4 IE 06
Noncancer
Child
Dose
(mg/kg-d)
63E 14
20E 12
26E 13
41E-12
92E 12
52E^)8
90E-1C
BOE-09
3 2E-08
71E-12
34E09
1 5E-10
1 5E-10
2 OE 08
92E09
3 OE-07
1 IE 09
\OE-07
32E09
73E09
2 6E-08
69E 06
52E 04
2 OE 05
1 5E 05
1 5E 05
Noncancer
School age
Dose
(mg/kg d)
38E-14
1 2E 12
16E 13
25E 12
56E-12
3 IE 08
55E 10
4 BE 09
1 9E 08
43E 12
2 1E-09
92E-11
92E 11
1 2E 08
56E 09
1 8E 07
65E 10
6 IE 08
1 9E 09
44E09
1 6E 08
42E 06
3 1E^)4
1 2E 05
94E 06
94E 06
fMoncancer
Farmer
Dose
(mg/kg d)
1 7E-14
54E-13
70E-14
1 1E-12
25E-12
1 4E-08
24E 10
2 IE 09
86E09
1 9E-12
92E 10
41E 11
4 IE 11
54E09
25E 09
8 IE 08
29E 10
2 7E 08
86E-10
20E09
69E09
IflE 06
1 4E 04
52E 06
4 IE 06
41E-06
NOTES
  NA • Not applicable
  NF - Not found
  NT • No loxicrty Information
  HQ • Hazard quotient
  HI * Hazard Index
 'olume V, Appendix V ' '
-------
TABLE 23  Maximum Iv   >5
34E^)5
1 2E 04
32E^)2
24E+00
9 1E^>2
72E 02
72E^)2
Subarea
W2max
W2 max
W2max
W2max

W2m»x
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2max
W2 max
W2max
W2max
W2max
W2max
W2max
W2max
Adult
Cancer
Risk
32E 11
1 OE 10
1 4E 11
2 1E-11
1 OE 09
NT
NT
1 4E-08
NT
20E-12
72E-10
22E-10
NT
NT
NT
NT
3 1E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
8 1E-11
26E 10
34E 11
52E 11
26E-09
NT
NT
3 4E-08
NT
51E-12
1 BE 09
54E-10
NT
NT
NT
NT
77E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancer
Risk
49E-11
1 6E-10
20E-11
32E 11
1 6E 09
NT
NT
2 1E 08
NT
3 IE 12
1 IE 09
32E-10
NT
NT
NT
NT
47E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
72E 11
23E 10
30E 11
4 7E 11
2 3E 09
NT
NT
30E-08
NT
46E-12
16E09
48E-10
NT
NT
NT
NT
69E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                             Adult      Child   School age   Farmer
                                                                                                                                           Noncancer Noncancer Noncancer  Noncancer
                                                                                                                                              HQ       HQ        HQ        HO
NT
NT
NT
NT
NT
NT
24E-06
2 8E-05
2 4E 04
1 5E 09
74E06
3 3E 08
1 6E-10
NT
NT
3 BE -03
5 BE 08
22E05
6 9E 07
1 IE 04
92E-08
37E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
90E 06
1 IE 04
90E04
5 7E-09
2 BE -05
1 2E 07
61E 10
NT
NT
1 4E 02
2 IE 07
8 IE-OS
26E06
42E04
34E07
1 4E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
55E 06
64E05
55E04
34E 09
1 7E-05
74E48
37E 10
NT
NT
8 5E-03 ,
1 3E-07
49E05
1 6E06
25E 04
2 IE 07
83E03
NT
NT
NT
Nl
NT
NT
NT
NT
NT
NT
24E06
2 BE 05
24E 04
1 5E 09
74E06
3 3E 08
1 6E-10
NT
NT
3 BE 03
58E08
2 2E 05
69E 07
1 IE 04
9 2E 08
3 7E 03
NT
NT
NT
NT
                                                                                Total Risk   23E08    5 8E 08    3 5E-08    5 1E-08
                                                                                                                                    Total HI   8 9E 03   3 3E 02   2 OE 02   8 9E 03
 NOTES.
   NA - Not applicable
   NF « Not found      v
   NT • No toxicHy Information
   HQ - Hazard quotient
   HI -Hazard Index
 Volume V. Appendix V-14
-------
 M C »fl ^? [ill.
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-------
                   t      (
TABLE 24  Maximum Initiation Risks and Noncancer HQs in Subarea W3
CHEMICAL
Acenaphthene
Acenaphthylana
Acetaldehyde
Acetone
Acetophenone
Acrylontbile
Anthracene
Benzene
Benzole acid
Benzotrlchjoride
Benzo(a)anth'racene
Benzo(n)pyrene
Benzo(b)fluorenthene
Ben*o(B,h.l)perylene
Benzo(k)fluoranthane
Bls(2-chloro«thoxy) methane
Bls(2-chloro«thyl)ether
Bls(2-chlorolsopropy1) ether
Bls(2-ethylhexyl)phthalate
Bromodichlofomettiano
Bromoform
Bromomethane
Bromodlph«ny1 ether p-
Butanone, 2- (Methyl ethyl ketone)
Butylbenrytphthalale
Carbon dlsulfide
Carbon lebachlortde
Chlofdane
Chloro-3-methylphenol, 4-
Chlotoaniline, p- (4-Chloroanlline)
Chlorobenzene
Chlorobenzilate
Chlotoothane (Ethyl chloride)
Chloroform
Chloromethane
Chloronaphthalene. beta
Chlotophenol. 2-
Chlorodiphenyl ether, 4- «.
Chrysene
Cresol. m-
Cresol, o- (2-Methylphenol)
Cresol. p-
Crotonaldehyd*
Cumene
DDE. 4.41-
Dibenz(a.h)anthracene
Dibromochloromethane
Dichlorobenzene. 1,3-
Dichlorobenzene, 1,4-
Dichlorobenzene. 1.2-
Dichlorobenzidme, 3.3'-
Dichlorobiphenyl
Inhalation
Slope
Factor
(mg/kg d)"-1
NA
NF
7 7E-03
NA
NA
2 4E-01
NA
29E-02
NA
NA
NA
NA
NA
NA
NA
NA
1 1E+00
NA
NA
NA
39E-03
NA
NA
NA
NA
NA
53E-02
1 3E+00
NF
NA
NA
2 7E-01
NA
8 1E 02
63E-03
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
RAC
(mg/m3)
00525
NF
000225
00875
00875
00005
02625
00015
35
NA
NA
NA
NA
NA
NA
NA
NA
0035
00175
00175
00175
000125
NA
025
0 175
00025
00005
0000053
NF
00035
0005
00175
25
000875
NA
007
0004375
NF
NA
0 04375
004375
0004375
NA
000225
NA
NA
00175
NA
02
005
NA
NA
Inhalation
RID
(mg/kg-d)
1 5E-02
NF
64E 04
25E 02
2 5E 02
1 4E 04
75E 02
43E-04
10E+00
NA
NA
NA
NA
NA
NA
NA
NA
1 OE 02
50E-03
50E 03
5 OE-03
36E-04
NA
7 IE 02
50E 02
7 1E-04
1 4EX)4
1 5E-05
NF
1 OE-03
1 4E-03
5 OE-03
7 1E-01
2 5E-03
NA
2 OE-02
1 3E-03
NF
NA
1 3E 02
1 3E-02
1 3E-03
NA
64E 04
NA
NA
50E 03
NA
57E 02
1 4E 02
NA
NA
Emission
Rale
(g/sec)
67E06
67E-06
30E-04
29E^>3
29E44
20E 04
55E-06
1 5E-05
1 IE 05
32E^5
55E-08
55E-06
55E-06
55E-06
5SEXW
87E^>6
1 3E 05
67E-06
37E05
1 OE-04
55E^)6
49E-04
87E-06
5 IE 05
55E^)6
89E 05
1 6E-04
55E-07
87E 08
87E 06
55E 06
37E 05
49E 04
2 7E 04
25E 04
67E06
55E 06
67E 06
55E 06
55E 06
55E 06
55E 06
1 4E 04
55E 06
55E 07
55E 06
26E 05
55E 06
55E 06
55E 06
33E 05
4 7E 08
Subarea
W3m«x
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3ma*
W3ma»
W3ma«
W3ma«
W3ma»
W3ma«
W3max
W3ma«
W3max
Adult
Cancer
Risk
NT
NT
55E-12
NT
NT
1 2E-10
NT
1 OE-12
NT
NT
NT
NT
NT
NT
NT
NT
35E-11
NT
NT
NT
5 1E-14
NT
NT
NT
NT
NT
20E-11
1 7E-12
NT
NT
NT
24E-11
NT
5 IE 11
37E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
IJT
NT
NT
NT
NT
NT
NT
tJT
Child
Cancer
Risk
NT
NT
1 4E 11
NT
NT
29E 10
NT
25E-12
NT
NT
NT
NT
NT
NT
NT
NT
87E-11
NT
NT
NT
1 3E-13
NT
NT
NT
NT
NT
50E-11
42E-12
NT
NT
NT
60E-11
NT
1 3E-10
92E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
fjf
NT
NT
School-age
Cancer
Risk
NT
NT
84E-12
NT
NT
1 7E-10
NT
1 5E-12
NT
NT
NT
NT
NT
NT
NT
NT
53E-11
NT
NT
NT
76E-14
NT
NT
NT
NT
NT
30E-11
26E-12
NT
NT
NT
36E-11
NT
77E-11
56E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
UT
NT
NT
f/T
NT
NT
Farmer
Cancer
Risk
NT
NT
1 2E-11
NT
NT
26E-10
NT
23E-12
NT
NT
NT
NT
NT
NT
NT
NT
78E-11
NT
NT
NT
1 1E-13
NT
NT
NT
NT
NT
44E-11
38E-12
NT
NT
NT
53E-11
NT
1 1E-10
82E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
UT
fJT
in
UT
MI
NT
UT
fH
Adult
Noncancer
HQ
8 3E-09
NT
8 7E-06
22E06
2 2E-07
26E05
1 4E 09
6 4E-07
2 1E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-08
1 4E-07
38E-07
20E08
26E-05
NT
13E08
20E09
23E-08
2 IE 05
6 8E-07
NT
1 2E-07
7 2E 08
1 4E-07
1 3E-08
20E-06
NT
62E-09
62E-08
NT
NT
82E4)9
82E09
8 2E 08
NT
1 6E 07
NT
NT
98E 08
tJT
1 BE 09
7 ?r 09
NT
111
Child
Noncancer
HQ
3 1E-08
NT
33E05
8 IE 06
82E 07
98E05
51E-09
24E-06
79E-10
NT
NT
NT
NT
NT
NT
NT
NT
4 7E 08
5 2E 07
1 4E46
77E-08
95E-05
NT
SOE-08
7 7E-09
87E06
77E05
26E-06
NT
4 7E 07
2 7E 07
5 IE 07
4 BE 08
74E-06
NT
2 3E 08
3 IE 07
NT
NT
3 IE 08
3 IE 08
3 1F 07
NT
6 OF 07
NT
HI
3 7F 07
tIT
6 J( 09
? 7f m
NT
til
School-age
Noncancer
HQ
19E-08
NT
20E05
49E 06
4 9E 07
59E05
31E-09
1 4E-06
48E-10
NT
NT
NT
NT
NT
NT
NT
NT
2 BE -08
3 IE 07
87E^>7
46E48
5 BE -05
NT
30E08
46E 09
52E06
47E05
15E-08
NT
28E 07
1 6E 07
3 IE 07
29E 08
45E06
NT
1 4E 08
1 9E 07
NT
NT
1 9E 08
1 9E 08
1 9E 07
NT
3BF. 07
NT
UT
2 ?F 07
NT
40E 09
1 r,F_ 08
NT
UT
Farmer
Noncancer
HQ
83E-09
NT
87E06
22E06
2 2E-07
26E05
1 4E 09
6 4E 07
2 1E-10
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 08
1 4E 07
3 BE 07
20E^W
26E-05
NT
t 3E 08
20E^)9
2 y. 06
2 IE 05
68Efl7
NT
1 2E 07
72E08
1 4E07
1 3E 08
20E06
NT
62E09
82E 08
NT
NT
82E 09
82E09
8 2E 08
NT
1 6F. 07
UT
NT
9 OF -08
NT
1 8E 09
7 ?F 09
(II
N1
/olume V, Appendix V-14
-------
TABl C 24  Maximum Inhalation Risks and tfoncancet HQs in Snbaiea W3
CHEMICAL (
Dichlorodifluofomathana
Dichlotoethana, 1,1- (Ethylidene dichlonde)
Olchloioathina, 1,2-
Dichlotoethana. 1,1- (Vinylidine chlonde)
Dlchloroathana (trans). 1 ,2-
Dichlorophanol. 2.4-
Dlchloropropane. \,i- (Propylene dichloride)
Dichloropropana (els). 1 3
Dlchloropropena (bans), 1 ,3-
Dlatny1phth«l«ta
Dlmethoxybvnzldma, 3,3'-
Dimathylphenol. 2.4-
Dlm»thytphtti»lat«
Dl n-buty1phlti«lat«
Dln*ololu«n». 2.6
1 DtnNro-2-tnathylphenol, 4.6-
Dlnttrophenol. 2,4-
~>inrbo(olue->e. 2,4-
, Xox»n«, 1.4-
)l(n)oc6
55E4»
1 6E4K
55E06
55E06
55E-06
55E^)6
49E^>4
55E-06
39Efl5
25Efl4
50EX)4
1 2E4)4
3 1E 05
1 5E 10
55EW
67E06
6 1E 04
55E06
55E-07
1 4E-08
55E-06
1 4E 08
1 OE 04
55E 05
55E 06
55E06
32E 05
64E 05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
4 2E 05
1 7E 08
55E 06
6 7E 06
6 7E 06
Subarea
W3max
W3m»x
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3mix
W3max
W3mix
W3max
\M3max
W3max
W3max
W3max
W3m«x
W3max
W3max
W3m«x
W3m»x
W3max
W3max
W3max
W3max
W3max
W3max
WSmax
W3msx
W3max
W3max
W3ma»
W3max
W3max
W3max
W3max
W3max
W3'max
W3max
W3max
W3max
W3 max
W3 max
Ofl-srte
Vapor
Cone
(ug'm3)
1 7E 05
85E 07
85E07
85E07
85E07
3 7E-07
8 5E 07
85E07
8 5E-07
1 1E-O6
78E-06
37E-07
37E-07
1 1E4>6
37E-07
3 7E-07
3 7E-07
3 7E-07
34E-05
37E-07
26E4)6
1 7E 05
34E-05
78E 06
2 1E-06
99E-12
37E^^
4 5E 07
4 IE-OS
37E-07
37E-08
95E-10
3 7E-07
95E-10
69E06
37E06
3 7E-07
3 7E-07
22E06
44E 06
3 7E 07
45E 07
78E 06
3 7E 08
85E 07
85E 07
2 7E 05
2 BE 06
1 IE 09
3 7E 07
4 5E 07
4 5E 07
Cancer
Adult
Dose
(mg/kg d)
59E 10
30E 11
30E 11
30E 11
30E 11
1 3E 11
30E-11
30E-11
30E 11
40E-11
28E-10
3E-11
3E-11
37E-11
3E-11
3E 11
3E-11
3E 11
1 2E-09
1 3E-11
93E 11
59E 10
1 2E 09
28E-10
73E-11
35E-16
13E-11
1 6E-11
1 5E 09
1 3E-11
1 3E-12
34E-14
1 3E-11
34E-14
24E 10
1 3E 10
1 3E-11
1 3E 11
77E-11
15E 10
1 3E 11
1 6E-11
28E 10
1 3E 12
30E 11
30E 11
95E 10
1 OE 10
4 OE 1 4
1 3E II
t 6E 11
1 BE It
Cancer
Child
Dose
(mg/Vg d)
t 5E 09
7 5E 11
75E-11
75E-11
75E 11
33E 11
75E-11
75E 11
75E 11
tOE-10
69E-10
33E-11
33E-11
93E-11
33E-11
33E-11
33E-11
33E-11
29E-09
33E-11
2 3E 10
1 5E 09
30E 09
69E-10
1 8E-10
8 7E-18
33E-11
40E-11
36E-09
33E 11
33E 12
84E 14
33E 11
84E-14
60E 10
33E-10
33E-11
33E 11
1 9E 10
38E 10
33E 11
40E-11
69E 10
3 3E 12
75E 11
75E 11
2 4E 09
2SE 10
99E 14
3 3E II
4 OE 11
4 OE 11
Cancer
School age
Dose
(mg/kg-d)
88E-10
45E-11
45E 11
45E-11
45E-11
20E 11
45E-11
45E-11
45E 11
6 1E-11
41E-10
20E-11
20E-11
56E-11
20E-M
20E 11
20E 11
20E 11
1 8E-09
20E-11
1 4E-10
8 BE 10
1 8E 09
4 1E-10
1 1E-10
53E-16
20E 11
24E-11
22E-09
20E-11
20E 12
50E-14
20E-11
SOE-14
36E 10
20E-10
20E 11
20E-11
1 2E 10
23E 10
20E 11
24E 11
4 1E 10
20E 12
45E 11
45E 11
1 4E 09
1 5E 10
60E 14
20E 11
? 4E 11
2 4F 11
Cancer
Farmer
Dose
(mg/Vg-d)
1 3E 09
6 7E 11
67E 11
67E-11
67E 11
29E 11
6 7E 11
67E 11
67E-11
90E-11
61E 10
29E 11
29E 11
83E-11
29E 11
29E-11
29E 11
29E-11
26E09
29E-11
2 IE 10
1 3E 09
27E-09
6 IE 10
16E-10
78E-16
29E 11
36E 11
32E09
29E 11
29E 12
74E-14
29E-11
74E 14
54E-10
29E 10
29E 11
29E 11
1 7E-10
34E 10
29E 11
36E 11
6 IE 10
29E 12
67E 11
67E11
2 1E 09
2?E 10
89E 14
29E 11
3 BE 11
i r>r H
Noncancer
Adult
Dose
(mg/kg d)
46E09
23E 10
23E 10
23E 10
23E 10
1 OE 10
23E 10
23E 10
23E 10
3 1E-10
2 IE 09
10E-10
10E 10
29E 10
10E 10
t OE 10
1 OE-10
10E 10
92E4»
1 OE-10
72E 10
46E09
93E 09
2 IE 09
57E-10
27E-15
1 OE 10
1 2E 10
1 IE 08
1 OE 10
10E 11
26E-13
1 OE-10
26E 13
1 9E 09
1 OE 09
1 OE-10
1 OE-10
60E 10
1 2E 09
1 OE 10
1 2E 10
2 1E 09
1 OE 11
2 3E 10
23E 10
7 4E 09
7 BE 10
^ IE 13
1 OE 10
1 ?E 10
1 ?F 10
Moncancer
Child
Dose
(mg/kg-d)
1 7E 08
87E 10
87E 10
87E-10
87E 10
38E 10
87E 10
87E 10
87E-10
1 2E 09
BOE-09
38E-10
38E-10
11E09
38E-10
3 BE 10
3 BE 10
3 BE 10
34E08
3 BE 10
27E-09
1 7E-08
35E08
80E09
2 IE 09
1 OE 14
3 BE 10
4 7E-10
4 2E 08
3 BE 10
38E 11
97E-13
3 BE 10
97E 13
70E 09
3 BE 09
3 BE 10
38E 10
22E 09
45E 09
3 BE 10
4 7E 10
80E 09
3 BE It
8 ?E 10
8 ?E 10
2 BE 08
29E 09
1 2E 12
3 BE 10
4 7E 10
4 7F 10
Moncancer
School age
Dose
(mg/kg-d)
1 OE 08
53E 10
53E 10
53E-10
53E 10
23E 10
53E-10
53E 10
53E 10
7 IE 10
4 BE -09
2 3E 10
23E 10
66E 10
23E 10
23E 10
23E 10
23E 10
2 IE 08
23E-10
16E09
1 OE 08
21E08
48E 09
1 3E 09
6 IE 15
23E 10
28E 10
26E 08
23E 10
23E 11
59E 13
23E 10
59E 13
42E 09
23E 09
23E 10
23E 10
1 3E 09
27E 09
23E 10
2 BE 10
4 BE 09
23E 11
53E 10
53E 10
1 7E 08
1 BE 09
70E 13
23E 10
2 BE 10
2 BE 10
Joncancet
Farmer
Dose
(mg/Vg d)
46E09
23E 10
23E 10
23E-10
23E 10
10E 10
23E 10
23E-10
23E 10
3 1E-10
21E09
1 OE-10
1 OE 10
29E 10
IDE 10
1 OE-10
10E 10
1 OE-10
92E09
1 OE 10
72E 10
46E09
93E 09
2 1Efl9
57E 10
27E 15
1 OE 10
12E 10
1 1EXJ8
1 OE 10
10E 11
26E-13
1 OE 10
26E-13
1 9E 09
1 OE^)9
1 OE 10
1 OE 10
60E 10
1 2E 09
1 OE 10
1 2E 10
2 IE 09
1 OE 11
2 3E 10
23E 10
7 4E 09
7 BE 10
3 IE 13
1 OE 10
1 2E 10
1 7F 10
  ume V Appendix V 14
-------
   TABtE 74  Maximum Inhalation Risks and Noncancoi MOi m Suhaioa W3
   CHEMICAL

   Dichlorodifluoromethane
   Dichloro«than«. 1.1- (Ethylidene dichlonde)
   Dich|oro«th»n«. I.?
   Dlchloroeth«n«. t.1- (Vinylidine chloride)
   Dich|oro«th«ne (trans), 1.2-
   Dlchloroph«nol. 2.4-
   Dlchtof opropana. 1.2- (Propylene dichlorld*)
   CMchlofopropane (els), 1,3-
   Dlchlof opr opana (bans) 1 3-
,   DIMhylphlhBiate
:   Dimethoxyb*nzldin«, 3.3'-
j   Dimalhylphwiol. 2.4-
'   Dtmaihylphthalata
j  Di-n-butytpMhalale
I  Dlnltrotoluene  26
  CMnitro-2-mathylphenol. 4.6-
j  Dinltrophenol. 2.4-
  Dlnttrotoluene. 2,4-
  Dloxana, 1.4-
  Dl(n)octy1 phlhalate
  D. 2.4-
  Ethyl mathacrylafe
  Ethylbanzana
  Ethylene dibromide
  Ethytene oxide
  Ethylena thk>ur«i
  Fluoranthane
  Fluor en*
  Formaldehyde
  Furfural
  Heptachlor
  H0ptachlorobiphanyf
  Hflxachloroberuena
  Hakachloroblphany)
  Hexachlorobutadlane
  Haxachlorocyclohaxana. gamma (Llndane)
  Haxachlotocyclopentadiene
  Hexachloroathana        v
  Haxachlorophena
  Hexinone. 2-
  nd»no( t ,2,3-cd)pyrene
  sophorona
 Maleic hydrailda
 Welhoxychlor
 Wettiyl-l-butyl ether
 ^ethyl-2-Pentanone, 4-  (MIBK)
 Welhylene chloride
 Wethylnaphlhalone 2-
 Wonochlorobiphenyl
 Slaphthalene
 "Jrtroamline 2-
"•Irtroaniline. 3-
Inhalation
Slope
Factor
(mg/kg-d)A-
MA
NA
9 IE 02
1 2E»00
NA
NA
NA
1 3E-01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
76E 01
35E 01
NA
NA
NA
45E-02
NA
45E»00
NA
1 6E»00
NA
7 BE -02
NA
NA
1 4E 02
NA
NF
NA
NA
NA
NA
NA
NA
1 6£ 03
NF
NA
NA .
NA
NF
RAC
1 (mg/m3|
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
OOO007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0175
04375
0004375
0 75
002
0 75
fJF
NA
0035
000005
NF
Inhalation
RfD
(mg/kg-d)
1 4E-02
36E 02
NA
2 3E-03
50E-03
75E 04
29E-04
t 4E 03
1 4E 03
20E-01
NA
50E-03
NA
25E 02
25E04
NF
50E 04
50E 04
NA
50E 03
25E 03
23E 02
7 IE 02
1 4E 05
NA
20E 05
10E 02
t OE 02
50E 02
36E 03
1 3E-04
NA
20E-04
NA
50E 05
75E-05
50E 06
25E04
7 5E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 1E 01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E 05
NF
Emission
Rate
(g/sec)
2 5E 04
1 3E 05
13E05
1 3E 05
1 3E-05
55E06
1 3E-05
13E05
1 3E-05
17E4K
1 2E-04
55E-06
55E^»
1 6E^)5
55E^6
55E06
55E06
55E 06
49E 04
55E-06
39E 05
25E^)4
50E 04
1 2E 04
3 IE 05
1 5E 10
55E06
87E-06
8 IE 04
55E06
55E07
1 4E 08
55E 06
1 4E 08
10E 04
55E 05
55E 06
55E 06
32E 05
64E-05
55E 06
6 7E 06
1 2E 04
55E 07
1 3E 05
1 3E 05
40E 04
4 2E 05
1 7E 08
55E 06
6 7E 06
6 ?E 06
Subaiea
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3ma>
W3ma«
W3ma«
W3max
W3ma»
W3ma<
W3ma»
W3 max
W3 man
W3 ma<
W3 max
W3 max
W3 max
W3 max
W3ma»
Adult
Cancer
Risk
NT
NT
27E 12
36E 11
NT
NT
NT
39E 12
39E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 IE 10
26E-11
NT
NT
NT
65E-11
NT
59E-12
NT
2 1E-11
NT
19E-11
NT
NT
1 8E-13
NT
NT
NT
NT
NT
NT
NT
NT
1 6E 12
NT
NT
NT
NT
NT
Child
Cancer
Risk
NT
NT
68E 12
89E-11
NT
NT
NT
97E 12
97E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
52E 10
64E-11
NT
NT
NT
1 6E-10
NT
1 5E-11
NT
53E-11
NT
47E-11
NT
NT
46E-13
NT
NT
NT
NT
NT
NT
NT
NT
39E 12
NT
in
NT
NT
NT
School-age
Cancer
Risk
NT
NT
4 IE 12
54E-11
NT
NT
NT
5 BE 12
58E 12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
32E 10
38E-11
NT
NT
NT
98E-11
NT
89E 12
NT
32E-11
NT
28E-11
NT
NT
28E-13
NT
NT
MT
fl I
fit
MT
1 4 1
fit
f JT

? 3F 12
fJI


NT
NT
Faimer
Cancer
Risk
NT
NT
6 1E 12
80E-11
NT
NT
NT
86E 12
86E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 /E 10
57E-11
NT
NT
NT
1 5E-10
NT
t 3E-11
NT
47E-11
NT
42E-11
NT
NT
41E-13
NT
NT
NT
1 1 T
N 1


f ) T
3 5F 1?
tl T

11 T
ft T
f 1 T
NT
   Adult      Child   School-age   Farmer
Noncancer  Noncancer Noncancer Noncancer
   HQ        HQ        HQ         HQ
32E 07
65E09
NT
1 OE 07
4 7E-08
1 4E-07
8 1E-07
t 6E-07
1 6E 07
16E-09
NT
20E-OB
NT
1 2E-08
41E-07
NT
2 OE 07
2 OE 07
NT
20E4W
2 9E-07
2 OE 07
1 3E 07
15E-04
NT
1 4E-10
1 OE 00
1 2E-08
2 3E 07
29E08
82E-08
NT
5 1E-07
NT
38E-OS
1 4E 05
20E-05
4 IE 07
79E-06
NT
NT
25E09
1 7E 08
82E09
1 IE 09
4 IE 08
34F. 08
NT
NT
t OF 08
8 7F 06
m
1 2E 06
2 4E 08
NT
39E 07
1 7E 07
5 IE 07
30E06
6 1E-07
61E-07
59E-09
NT
77E-08
NT
44E08
15E-06
NT
7 7E 07
7 7E-07
NT
77E-08
1 IE 06
76E 07
49E 07
56E-04
NT
5 IE 10
3 BE 08
4 7E 08
8 4E 07
1 IE 07
31E 07
NT
19E-06
NT
1 4E 04
5 IE 05
7 7E 05
15E06
30E 05
NT
NT
93E 09
64E 08
3 IE 08
4 IE 09
1 5E 07
1 IF 07
NT
NT
3 BE 08
3 
-------
TABLE 24  Maximum Inhalation Risk-; and Noncancci MQs in Subaioa W3
CHEMICAL
Nitioanilin«.4-
^itiobenzena
Jitrophenol. 2-
-litoophenol. 4
4 Ntboso dt n butylamlne
J Niboso-dl n propylamin«
4 Nitjosodiphenylamina (Diphenylamine)
Jonachlorobiphenyl
Dctachlorobiphanyl
3ent»chk>roberur«ne
'entachloroblphenyl
'entachlofonNiobanzene
'entachtorophenol
'hananthrena
'h«nol
*y'*n*
,»fTol« (5-(2-Prop«nyl) 1 ,3 ben/odioxole)
ityrene
ebachlorobiphenyl
abachloro«thane. 1.1 1 2-
abachloroethane. 1.1.2 2-
ebachloroethene
ebachlorophenol. 2.3.4.6-
oluene
. rkhk>ro-1,2.2-trffluofoethane. 1.1,2
, rfchtorobanzene. 1 2.4
I rlchlorobiphanyl
; rtcnloroethane. 1 , 1 , t - (Methyl chlorolorm)
1 rlehloroathana, 1,1.2 •
rlchloroethene
; rtcntorofluofomelhana
1 rlchlorophanol, 2.4.5-
fichlorophenol, 2,4,6-
Inyl acetate
my) chloride
/lene, m/p- (m/p-Dim«thy< benzene)
/lene. o- (o-Dlmettiyl benzene)
%.
, 3,7.8-TCDO
2.3.7.8PCDD
2 3.4.7.6 HxC DO
2.3 6.7.8 HxCDD
2.3,7.8 9-HxCOO
2.3,4.6.7,8-HpCDD
CDO
3 78 TCDF
2 3 7.8 PCDF
3 4 7.8-PCDF
23478 HxCDF
23678 HrCDF
34678 HxCDF
Inhalation
Slope
Factor
(mg/kg d)A-1
NF
NA
NF
NF
54E«00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E4)2
20E-01
20E-03
NA
NA
NA
NA
NA
NA
57EXJ2
60E-03
NA
NA
10E-02
NA
30E-01
NA
NA
1 5E+05
7 5E»04
5E«04
5E»04
5E«04
5E«03
5E'02
5E*04
75E»03
7 5E»04
1 5E*04
1 5E'04
1 5E*04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
002625
NA
000875
0 02625
0 1
75
005
fJA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfO
(mg/kg d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E^)1
75E-03
NF
7 1E-02
NA
75E4>3
NA
25E^)3
75E 03
29E^)2
2 1E«00
1 4E^2
NA
7 1E 02
1 OE-03
NA
50E4J2
25E-02
NA
1 4E^>2
NA
50E 01
50E 01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
Emission
Rate
(g/sec)
67E 06
55E 06
67E 06
55E 06
1 2E 04
67E06
67E-06
1 4E-06
1 4E-08
48E-05
1 4E 08
34E-05
55E06
87E-06
55E06
55EO6
1 2E 04
23E-05
1 4E 0«
55E-06
55E-06
5 IE 05
6 BE -06
6 1E04
33E^)4
55E 06
30E 08
13E4>5
1 3E 05
1 9E-05
25E 04
55E06
55E 06
64E 05
25E 04
38E 04
55E-06
1 08E 1 1
678E 11
8 95E 1 1
1 66E 10
1 09E 10
1 24E 09
6 1 5E 09
8 77E 11
3 45E 10
4 67E 10
1 43E 09
1 33E 09
1 SOE 09
Subarea
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
\nT3max
W3max
W3m«x
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3miw
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3ma
W3ma
W3ma
W3ma
W3ma
W3ma
W3ma
W3 ma
W3ma
VV3 ma
W3ma
W3 ma
W3 ma«
Ofl site
Vapor
Cone
(ug/m3)
45E 07
3 7E 07
45E 07
3 7E-07
62E 06
45E-07
45E^)7
95E 10
95E 10
32E-06
95E 10
23E 06
3 7E-07
45E07
3 7E 07
37E 07
78E 06
1 5E 06
95E 10
37E-07
3 7E 07
35E 06
46E^)7
42E^)5
22E05
3 7E 07
2 1E 09
BSE 07
85E-07
1 3E-06
1 7E-05
37E 07
3 7E-07
44E 06
1 7E 05
2 6E 05
3 7E-07
73E 13
46E 12
6 IE 12
1 1E 11
74E 12
84E It
4 2E 10
60E 12
2 3E 11
3 2E II
9 7E 11
9 IE 11
1 OE 10
Cancel
Adult
Dose
(mg/kg-d)
16E 11
3E-11
6E 11
3E 11
9E-10
6E-11
6E-11
34E 14
34E 14
1 1E 10
34E-14
8 1E-11
1 3E-11
16E 11
1 3E 11
1 3E-11
28E 10
54E-11
34E 14
1 3E-11
1 3E 11
1 2E-10
1 6E-11
1 5E-09
79E 10
1 3E 11
72E-14
30E 11
30E 11
45E-11
59E-10
1 3E-11
1 3E-11
1 5E-10
59E-10
9 1E-10
1 3E-11
26E 17
1 6E 16
2 IE 16
40E 16
26E 16
30E 15
1 5E 14
2 IE 16
6 3E 16
1 IE 15
3 4E 15
32E 15
36E 15
Cancel
Child
Dose
(mg/kg d)
40E 11
33E 11
40E-11
33E 11
7 2E-10
40E 11
40E 11
84E 14
84E 14
28E-10
84E 14
20E-10
33E-11
40E-11
33E-11
33E-11
69E-10
1 3E-10
84E-14
33E 11
33E 11
3 IE 10
4 1E-11
37E09
20E-09
33E-11
1 BE 13
75E-11
75E-11
1 1E-10
1 5E-09
33E-11
33E-11
38E-10
1 5E 09
2 3E 09
33E 11
64E 17
40E 16
53E 16
99E 16
6 5E 16
7 4E 15
3 7E 14
52E 16
2 IE 15
28E 15
8 5E 15
80E 15
90E 15
Cancel
School age
Dose
(mg/kg-d)
24E 11
20E 11
2 4E 11
20E-11
4 4E 10
24E 11
24E 11
50E-14
50E-14
1 7E-10
50E 14
1 2E-10
20E-11
24E-11
20E-11
20E 11
4 1E-10
8 1E-11
50E-14
20E-11
20E-11
1 BE 10
25E 11
22E-09
1 2E-09
20E 11
1 IE 13
45E 11
45E 11
67E-11
88E-10
20E-11
20E-11
2 3E-10
88E-10
1 4E^>9
20E-11
39E 17
24E 16
32E 16
60E 16
39E 16
45E 15
2 2E 14
3 2E 16
1 2E 15
1 7E 15
5 IE 15
4 BE 15
54L 15
Cancel
Farmer
Dose
(mg/kg d)
36E 11
29E 11
36E 11
29E-11
64E 10
36E 11
36E 11
74E 14
74E 14
25E-10
74E-14
1 6E-10
29E-11
36E-11
29E-11
29E 11
61E-10
1 2E-10
74E-14
29E 11
29E 11
2 7E 10
36E 11
33E^)9
18E 09
29E 11
1 6E 13
67E-11
67E 11
99E 11
1 3E-09
29E-11
29E 11
34E-10
1 3E-09
20E 09
29E 11
57E 17
36E 16
4 BE 16
8 BE 16
58E 16
66E 15
3 3E 14
4 7E 16
1 BE 15
2 5E 15
7fiF 15
7 If 15
B Of 1 r>
Noncancei
Adult
Dose
(mg/kg d)
1 2E 10
10E 10
1 2E 10
10E-10
23E09
1 2E 10
1 2E 10
26E 13
26E 13
89E 10
26E 13
63E-10
10E 10
12E-10
10E 10
1 OE 10
2 1E^)9
42E 10
26E 13
IDE 10
1 OE 10
96E 10
1 3E 10
1 1E-08
61E-09
10E-10
56E 13
23E-10
23E 10
35E 10
46E09
IDE 10
1 OE-10
12E-09
46E09
7 IE 09
1 OE-10
20E 16
1 3E 15
1 7E 15
31E 15
20E 15
2 3E 14
1 1E 13
1 6E 15
64E 15
8 7E 15
2 7E 14
25E 14
?BF 14
Noncancei
Child
Dose
(mg/kg d)
4 7E 10
3 BE 10
4 7E 10
38E 10
84E09
47E 10
47E 10
97E-13
97E 13
33E09
97E-13
23E 09
3 BE 10
47E -10
38E-10
3 BE 10
80E09
16E 09
97E 13
38E-10
38E 10
36E-09
47E 10
43E08
23E08
3 BE 10
2 IE 12
87E 10
87E 10
1 3EO9
1 7E 08
3 BE 10
38E 10
45E09
1 7E 08
26E 08
38E-10
75E 16
4 7E 15
62E-15
1 2E 14
76E 15
B6E 14
4 3E 13
6 IE 15
2 IE 14
3?E 14
99E 14
9 3F 14
i OF n
Noncancei
School age
Dose
(mg/kg d)
28E-10
23E 10
2 BE 10
23E 10
5 IE 09
2 BE 10
28E 10
59E 13
59E 13
20E09
59E 13
1 4E 09
23E 10
2 BE 10
23E 10
23E 10
4 BE 09
95E 10
59E 13
23E 10
23E 10
22E 09
29E 10
26E 08
1 4E 08
23E 10
1 3E 12
53E 10
53E 10
7 BE 10
10E 08
23E 10
23E 10
2 7E 09
1 OE 08
1 6E 08
2 3E 10
45E 16
29E 15
38E 15
70E 15
46E 15
52E 14
26E 13
3 7E 15
1 4E 14
20E 14
60E 14
56E 14
6 IF 14
Noncancer
Farmer
Dose
(mg/kg-d)
1 2E 10
1 OE 10
1 2E 10
1 OE 10
23E09
1 2E 10
1 2E 10
26E 13
2 BE 13
89E 10
26E 13
63E 10
10E 10
12E 10
1 OE-10
1 OE-10
2 IE 09
42E 10
26E-13
1 OE 10
1 OE-10
96E 10
1 3E 10
1 1E4B
61E-09
1 OE-10
56E 13
23E 10
23E 10
35E 10
46EO9
10E 10
10E 10
12E09
46E-09
71E09
1 OE 10
20E 16
1 3E 15
1 7E 15
31E 15
20E 15
23E 14
1 IE 13
1 6E 15
64E 15
8 7E 15
2 7E 14
25E 14
7BF 14
  lume V. Appendix V 1'
-------
                   V,   )
TABLE 24  Maximum Inhalation Risks and Noncancei HQs in Subaiea W3
CHEMICAL
Ntooanlllne, 4-
Nibobeniene
Nrbophenol. 2-
Nrbophenol, 4-
N Nitioso-dt-n-butyl«mlne
N Nitioso-dl-n-propylamlna
N Nrbosodlphenylamlne (Ophenylamlne)
NonachloroblpJienyt
Octachtoroblphanyl
P»nt»chlofob»nzana
Pantachlwoblphanyl
Pant«chlotonltrob«nzan»
Pantachltxophvnol
PhenanBvene
Phenol
Pyrena
Safrole (5-(2-Propenyf)-1.3 benzodioxole)
Slyrana
Tetrachloroblphenyl
Tetrachloroethane. 1.1,1 2-
Tatrachlorcrathana. 1.1.2.2
T«tr»chloioethena
Talrachlorophanol. 2.3.4.6
Toluan*
Ttlchloro-1.2,2-tirfluotoeth8ne. 1,1.2-
Trichtorobenzene, 1,2.4-
Trtchloroblphenyl
Tr1chloro«than«. 1 .1 ,1- (Methyl chloiolorm)
Trtchloroalhana, 1,1.2-
Trlchloroethene
Trtchlorofluoromathana
Trichlorophenol. 2.4.5-
Ttlchlorophanol, 2.4,6-
\flnyl acetate
Vinyl chlorida
Xytene. m/p- (nVp-CMmethyl benzene)
Xylana, o- (o-Dlmethyl benzene)
2,3.7.8-TCDO
1.2, 3,7.6 PC DO
1 ,2 3,4.7 8 HxCDO
1.2, 3.6. 7.8 HxCDO
1.2.37 8.9HxCDD
1.2346 78-HpCDD
OCDD
2,3.7,8 TCDF
1,2. 3,7,8 PCDF
2.3.4. 7,8 PCDF
1.234.7,8HxCDF
123678 HxCDF
? 346,78 HxCDF
Inhalation
Slope
Factor
(mg/Vg d)*-1
NF
NA
NF
NF
54E»00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
2 6E 02
20€^)1
20€ 03
NA
NA
NA
NA
NA
NA
57E-02
60E-03
NA
NA
1 OE^)2
NA
30E-01
NA
NA
1 5E«05
75E*04
1 5E+04
1 5E»04
1 5E»04
1 5E»03
1 5E»02
1 5E»04
75E«03
75E«04
1 5E«04
1 5E«04
1 5E*04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
002625
NF
025
NA
002625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
HA
NA
NA
NA
NA
NA
NA
HA
HA
NA
Inhalation
RID
(mg/Kg-d)
NF
1 4E-04
NF
NF
NA
NA
NA
NA
NA
NA
NA
7 5E 04
75E-03
NA
1 5E 01
75E-03
NF
7 1E 02
NA
75E 03
NA
25E 03
75E 03
29E 02
2 1E»00
1 4E-02
NA
7 1E 02
1 OE-03
NA
50E-02
25E 02
NA
1 4E 02
NA
50E 01
50E-01
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
tIA
NA
HA
Emission
Rata
(g'sac)
67EXW
55E06
6 7E4J6
55E^)6
1 2E44
67E06
6 7E-06
1 4E 08
1 4E-08
48E45
t 4E-08
34E-05
55E-06
67E^6
55EXJ6
55E-06
1 2E«4
23E^»
1 4E 08
55E-06
55Efl8
51E-05
6 BE 06
6 IE 4)4
3 3E^)4
55E^)6
30E^)8
1 3E^>5
1 3EX»5
1 9E4K
25E434
55E^)6
55E^6
64E^)5
25E^>4
3 BE 04
55E-06
1 08E-11
678E 11
895E It
1 66E 10
1 09E 10
t 24E 09
6 15E 09
8 77E 11
345E 10
467E 10
1 43E 09
1 33E 09
f 50E 09
Subarea
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3ma»
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3ma»
W3max
W3ma<
W3ma»
W3 max
W3 ma«
W3 ma»
W3 ma«
W3 ma«
W3 ma«
W3 ma«
W3 ma«
W3 ma<
W3 ma«
W3 ma«
Adult
Cancer
Risk
NT
NT
NT
NT
1 6E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
34E 13
2 7E-12
25E-13
NT
NT
NT
NT
NT
NT
1 7E 12
27E-13
NT
NT
1 3E-13
NT
1 8E-10
NT
NT
39E 12
1 2E 11
32E 12
59E 12
39E 12
4 5E 12
2 ?E 12
3 IE 12
6 2E U
8 4E 11
5 IE 11
4 8E 11
5 4f II
Child
Cancer
Risk
NT
NT
NT
NT
39E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
BSE 13
67E 12
62E 13
NT
NT
NT
NT
NT
NT
42E-12
66E-13
NT
NT
33E-13
NT
44E-10
NT
NT
97E 12
30E 11
80E 12
1 5E 11
97E 12
1 IE 11
55E 12
78E 12
1 5E 11
2 IE 10
1 3E 10
1 2E 10
1 3E 10
School age
Cancer
Risk
NT
NT
NT
NT
2 4E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 1E-13
40E-12
38E-13
NT
NT
NT
NT
NT
NT
26E 12
40E-13
NT
NT
20E-13
NT
26E-10
NT
NT
58E 12
1 8E 11
4 BE 12
90E 12
59E 12
6 7E t2
3 3E 12
4 ?E 12
9 3E 12
1 3E 10
7 7E 11
7 ?E 11
8 IE M
Farmer
Cancer
Risk
NT
NT
NT
NT
35E 09
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
76E-13
59E 12
55E-13
NT
NT
NT
NT
NT
NT
3 BE 12
59E-13
NT
NT
29E-13
NT
39E-10
NT
NT
8 BE 12
2 7E-11
7 IE 12
1 3E 11
8 7E 12
99E 12
49E 12
OE 12
4E 11
9E 10
IF 10
IF 10
?f 10
                                                                                                                                            Adult      Child    School age  Farmer
                                                                                                                                          Noncancer Noncancer  Noncancer Noncancer
                                                                                                                                             HQ       HQ        HO        HQ
NT
7 2E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 4E 07
1 4E-08
NT
68E-10
1 4E-08
NT
59E09
NT
1 4E-08
NT
38E07
1 7E-08
40E07
29E-09
72E-09
NT
33E 09
2 3E-07
NT
9 IE 08
41E-09
NT
84E08
NT
1 4E-00
20E-10
NT
NT
NT
NT
NT
NT
NT
Nt
NT
NT
in
NT
m
NT
2 7EJ)6
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 1E^)6
51E-08
NT
26E-09
51E^)8
NT
22E-08
NT
5 IE-OB
NT
1 4E-06
6 3E 08
15E 06
t IE 08
27E-08
NT
r 2E 08
67E-07
NT
34E 07
1 5E 08
NT
31E4)7
NT
53E08
7 7E 10
NT
NT
NT
fll
NI
m
NT
in
111
111
III
III
in
NT
1 6E 06
NT
NT
NT
NT
NT
NT
NT
NT
NT
19E-06
3 1E-08
NT
15E 09
3 IE 08
NT
1 3E-08
NT
3 1E-08
NT
66E07
3 BE 08
90E 07
65E09
1 6E-08
NT
7 4E 09
53E07
NT
2 IE 07
93E 09
NT
1 9E 07
NT
32E08
46E 10
NT
NT
NT
NT
NT
m
NT
NT
(IT
m
NT
III
111
NT
72E-07
NT
NT
NT
NT
NT
NT
NT
NT
NT
84E4)7
1 4E-08
NT
68E-10
1 4E-08
NT
59E-09
NT
1 4E-08
NT
38E07
1 7E^8
40E 07
29F 09
72E^)9
NT
33E09
23E47
NT
9 lEOfl
4 1E 09
NT
84Efl8
NT
1 4E 08
20E 10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
III
HI
/olume V. Appendix V 14
-------
".BLE 24  Maximum Inhalation Risks and Noncancei HQs in Subatea W3
:HEMICAL
.2.3.7.8.9 HxCDF
.2.3.4.6. 7.8-HpCDF
.2.3.4. 7.8,B-HpCDF
>CDF
Dtoxln TEQ
lumlnum
/iHmony
rsenlc
irlum
•rytlium
•dmlurn
hromlum (hexavalent)
htomlum (trlvalent)
OPP"
..ad
lercury (ind MeHg)
Ickel
ektnlum
ltv«f
hellium
Inc
ydrogen chloride
M*\ nitrogen oxides (NOx)
Dial sulfur oxides (SOx)
articulate matter
•spfrable particulates
Inhalation
Slope
Factor
(mg/kgd)A-1
1 5E»04
1 5E+03
1 5E«03
1 5E+02

NA
NA
50
NA
84
6 1
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mpj/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0 004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg-d)
NA
NA
NA
NA

NA
10E -04
75E-05
36E4>5
1 3E-03
1 3E-04
1 3E-03
25E-01
NA
NA
2 1E-05
50E-03
1 3E^)3
1 3E^)3
1 BE^»
75EO2
50E-04
NA
NA
NA
NF
Emission
Rat*
(g/s«e)
293E-10
9 30E-09
1 22E 09
1 89E 08
4 2BE-08
24E4M
42E-06
37E-05
1 SE-04
33E-08
1 6E-05
7 1E-07
71E-07
94E-05
43E05
1 4E-03
50E-06
47E-04
1 5E-05
34E-05
1 2E-04
32E-02
24E+00
9 1E-02
7 2E-02
72E-02
Subarea
W3max
W3 max
W3max
W3max

W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3max
W3m«
W3max
W3max
WSmax
W3max
Ofl site
Vapor
Cone
(ug/m3)
20E-11
6 3E-10
63E 11
1 3E^>9

1 BE -05
29E-07
25E06
IDE -05
22E-09
1 1E-06
48E-08
48E^>8
64E-06
29E-06
95E-05
34E-07
32E-05
1 OE 06
23E-06
82E-06
22E-03
1 6E-01
62E-03
4 9E 03
49E-03
Cancer
Adult
Dose
(mg/kg-d)
70E-16
2 2E-14
29E-15
45E 14
10E-13
57E-10
10E-11
89E-11
36E 10
79E-14
38E-11
1 7E-12
1 7E-12
23E-10
1 OE-10
34E-09
12E-11
1 1E-O9
36E-11
6 1E-11
29E-10
77E-08
58E-06
22E-07
1 7E-07
1 7E-07
Cancer
Child
Dose
(mg/kg-d)
1 7E-15
5 5E - 1 4
7 3E 15
1 1E-13
26E-13
1 4E-09
25E-11
22E-10
89E-10
20E-13
95E-11
42E-12
42E-12
56E-10
2 6E-10
64E-09
30E-11
2 BE -09
89E-11
20E-10
72E-10
19E-07
14E^)5
54E-07
43E-07
4 3E-07
Cancer
School-age
Dose
(mg/kg-d)
1 IE-IS
3 4E-14
44E-15
68E 14
1 5E-13
87E-tO
15E-11
1 3E-10
54E-10
1 2E-13
58E-11
26E-12
26E-12
34E-10
1 5E-10
50E-09
16E-11
1 7E-09
54E-11
1 2E-10
43E-10
12E-07
87E-06
33E-07
2 6E-07
26E-07
Cancer
Farmer
Dose
(mg/kg-d)
16E-15
S OF 14
J UC 1 •(
65E 15
1 OE-13
23E-13
1 3E-09
22E-11
2 OE-10
8 OE-10
1 8E-13
85E-11
38E-12
38E-12
5 OE-10
23E-10
74E-09
27E-11
25E09
80E-11
1 8E-10
64E-10
1 7E-07
1 3E^K
48E-07
38E-07
38E-07
Noncancer
Adult
Dose
(mg/kg-d)
55E 15
1 7P 11
1 1 C- 1 O
23E 14
35E-13
8 OE-13
45E-09
7 BE 11
69E-10
28E-09
6 IE 13
3 OE-10
13E-11
1.3E-11
1 SE-O9
BOE-10
26E-08
93E-11
88E-09
2 BE 10
63E-10
22E^9
60E-07
4SE4S
17E^»
1 3E-06
1 3E-06
Noncancer
Child
Dose
(mg/kg-d)
20E-14
6 5E-13
85E 14
13E 12
30E-12
17E-08
29E 10
26E-09
10E08
2 3E-12
1 IE 09
49E-11
49E-11
65E-09
30E-09
B7E-06
35E-10
33E-08
10E09
24E-09
84E-09
22E4)6
1 7E^4
63E-06
50E-06
50E-08
Noncancer
School-age
Dose
(mg/kgd)
1 2E-14
•1 QC f)
-------
     24  Maximum Inhalation Risks and Noneancef HOs in Suhatpa W3
MEMICAL
2.3.7.8.9 HxCDF
23 4 6,7.8 HpCDF
2.3.4.7.8,9 HpCDF
•CDF
Dioxin TEQ
lumlnum
ndmony
rsenlc
arlum
•rytllum
•dmlum
hromlum (hexavalent)
tvomlum (trtvalent)
opp«i
ead
(ercury (and MeHg)
llckel
elenlum
llvel
halllum
Ine
lydrogen chloride
ota! nitrogen oxides (NOx)
otal sulfur oxide? (SOx)
'articulate matter
tesplrable partculates
Inhalation
Slope
Factor
(mg/kgd)* 1
1 5E«04
1 5E»03
1 5E+03
t 5E«02

NA
NA
50
NA
64
81
4t
NA
NA
NA
NA
094
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
OOOO061
02625
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg d)
NA
NA
NA
NA

NA
1 OEX)4
75E 05
36E 05
1 3E^)3
1 3E 04
1 3E 03
2 5E 01
NA
NA
2 1E05
50E 03
1 3E 03
1 3E 03
1 BE 05
75E 02
50E 04
HA
NA
NA
NF
Emission
Rat*
(g/sec)
293E 10
930E 09
1 22E 09
1 89E^)8
428E4W
24E^>4
42E-06
37E05
1 5E-04
33E-08
1 6E4K
7 1E-07
7 1E-07
94E 05
43E 05
1 4E4)3
50EXM
4 7E^)4
1 5E^)5
34E-05
1 2E-04
32E 02
2 4E»00
9 1E^)2
72EXJ2
7 2E 02
Subarea
W3max
W3max
W3max
W3max

W3max
W3m.x
W3max
W3max
W3max
W3mix
W3m«x
W3m«x
W3max
W3 max
W3max
W3 max
W3 max
\n/3max
W3max
W3max
W3mM
W3max
W3 max
W3 max
W3max
AduH
Cancer
Risk
1 1E-11
33E 11
44E 12
68E 12
34E-10
NT
NT
44E-09
NT
66E-13
23E-10
70E-K
NT
NT
NT
NT
1 OE M
NT
NT
NT
NT
NT
NT
NT
NT
NT
Child
Cancer
Risk
2 6E 11
8 3E 11
1 IE 11
1 7E It
84E tO
NT
NT
1 IE 08
NT
1 7E-12
58E-10
1 7E-10
NT
NT
NT
NT
25E 11
NT
NT
NT
NT
NT
NT
NT
NT
NT
School age
Cancel
Risk
1 6E 11
50E-11
66E 12
1 OE M
5 1E-10
NT
NT
67E-09
NT
1 OE 12
35E-10
1 OE-10
NT
NT
NT
NT
1 5E It
NT
NT
NT
NT
NT
NT
NT
NT
NT
Farmer
Cancer
Risk
2 3E 11
74E <1
97E 12
1 5E tl
75E 10
NT
NT
98E-09
NT
1 5E 12
52E-10
1 5E-10
NT
NT
NT
NT
22E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
                                                                                                                                               Adult      Child    School age   Farmei
                                                                                                                                            Noncancei  Noncancet  Noncancei Noncancer
                                                                                                                                               HO        HQ        HO       HQ
NT
NT
NT
NT
NT
NT
7 8E 07
92E-06
78E-05
49E-10
24E-06
1 1E-06
53E-11
NT
NT
1 2E^)3
19E 08
70E^)6
22E^>7
36E^5
30E4»
1 2E-O3
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
29E 06
3 4E 05
29E04
1 8E09
89E 06
40E08
20E 10
NT
NT
45E03
70E 08
26E 05
84E 07
1 4E 04
1 1E 07
4 5E 03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 8Efl6
2 IE 05
1 8E 04
1 IE 09
54E06
2 4E 08
1 2E 10
NT
NT
2 7E 03
42E 08
1 6E 05
50E07
B2E^)5
6 7E 08
27E^3
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
78E^)7
92E^)6
78E^)5
49E 10
24Efl6
1 1E^J8
53E 11
NT
NT
1 2E 03
t 9E 08
70E 06
22E07
36E OS
30E OB
1 2E^)3
NT
NT
NT
NT
                                                                               Total Risk    75E-09    1 9E 08    1 IE 08    1 7E 08
                                                                                                                                     Total HI    29E03    1 IE 02    6 5E 03   2 9E 03
K3TES
 NA - Not applicable
 NF - Not found        ^
 NT > No toxtctty Information
 HQ - Hazard quotient
 HI - Hazard Index
nlumn V Appendix V 14
-------
                             APPENDIX V-15

                Estimation of Cancer Risks and Hazard Indices for
         Indirect Exposure Pathways for Subsistence Farmer in Subarea El
Volume V
-------
DIOXIN TEQ
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                                                                                      D| S ?
                                                                                      ££l»
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                                                                                      -111
                                                                                      ?
                                             =• ?
                                            j; -s -
TOTAL
CANCER
RISK
-------
      Avg C.»t»( HI Risk1. .im( No
                                      MOs  Adult 5n(isl-.fiMii i- f .iimi'l
                                        NONCARCINOGENIC HA7ARD QUOTIENTS
         Chemical
3 78 TCDO
2378 PeCDO
2 34 7.8 HxCDD
2.36 7.8 H«CDD
2 37 8 9 HxCDD
2.3,4.6.7.8 HpCDD
CDD
378 TCDF
2 3 7 B PeCDF
34.78 PeCDF
2 34.78 HxCDF
2 36 7.8 HxCDF
2 3 7 8 9 HxCDF
346 7,8 HxCDF
2 34.6,78 HpCDF
2 3.4 7.8.9 HpCDF
CDF
tliachlornbiphenyl
iiachlofobiphmiyl
uplachloiobiphenyl
)run(i)pyl»ne
m{o(b)ITuoianlhene
aibon letiachlofide
iban;(a,h)anlhiacena
i(n)octy1 phlhalale
aplachloi
flxachlotoben/ene
exachtofobuladwne
axachlofncyclopenladiene
exachlni opbane
d*no(1,2.3-cd)pyiBne
ntimony
i same
jfium
atyllium
admium
hiomium (hexavalent)

ifltcury
ii kel
fllenium
ilvet
hjlhuin
i or

DIOXIN TEQ
ORGANICS TOTAI (mm dinnii)
INORGANICS TOTAL
             SUBAREA TOTAL
Suhaiaa
ET avg
Et avg
El avg
E1 avg
El avg
El avg
E1 avg
El avg
El avg
E1 avg
E1 avg
El avg
Et avg
Et avg
Et avg
Et avg
Et avg
El avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
E1 avg
Etavg
El avg
El avg
E 1 avg
E 1 Jvg
E 1 avq
E 1 avg
i") E 1 avg
El avg
AL E 1 Jvg
Soil
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
99E tt
1 9E48
NT
2 BE 11
2 2E 11
2 7E-08
29E 07
14E 10
1 2E-07
NT
6 IE 09
32E07
1 7E 09
50E 11
2 BE 09
t 3E 09
NT
3 7E 06
4 BE 10
36E 07
1 BE 09
63E 06
2 1E 10
NT
46E 07
1 IE 05
1 IE 05
Soil
Deimal
Conlacl
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
HJ
NT
NT
NT
NT
NT
1 IE 10
2 IE 08
NT
3 IE 11
2 4E 11
29E 08
32E 07
1 5E 10
1 3E 07
NT
1 IE 09
5 7E 08
30E 10
9 IE 12
50E 10
24E TO
NT
66E 07
8 7E 11
65E 08
3 2E 10
t IE 06
3 8E 11
NT
50E 07
1 9E 06
2 4E 06
Beel
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 9E 04
2 8E 09
NT
5 IE 04
59E 08
36E 07
2 ?E 07
4 BE 10
92E 04
NT
72E 08
1 BE 08
22E 09
62E 11
3 IE 08
79E 09
NT
44E 06
1 IE 08
2 2E 06
7 3E 08
2 3E 04
7 3E 10
NT
1 6E 03
2 4E 04
1 9E 03
Poik
Ingaslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
52E 06
46E 10
NT
1 4E OS
1 BE 09
TOE 07
92E 08
T 6E 10
2 3E-05
NT
1 2E 08
2 3E 07
40E 09
1 9E 11
5 BE 10
3 7E 09
NT
60E 06
19E 08
2 IE 05
6 7E 10
3 3E 04
7 9E 11
NT
4 2E 05
36E 04
40E 04
Chicken
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 3E 13
2 BE 12
NT
3 BE 11
48E 13
26E 10
25E 10
4 IE 13
49E 08
NT
1 3E 10
1 3E 07
2 IE 12
1 OE 12
34E 09
59E 11
NT
1 6E 06
4 1E 11
94E 07
1 1E 11
9 ?E 05
9 7E 11
NT
4 9E 08
95E 05
9 5E 05
Olhei
Pnulliy
Ingoslinn
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
63E 14
7 7E 13
NT
1 OE It
1 3E 13
7 IE 11
6 BE 11
1 IE 13
1 3E^»
NT
34E 11
34E08
5 BE 13
28E 13
9 IE 10
1 6E It
NT
43E 07
1 IE 11
25E 07
3 IE 12
2 5E 05
2 6E 11
NT
I 3E 08
2 6E 05
2 6E 05
Egg
digestion 1
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 10
1 6E 09
NT
2 2E 08
2 BE 10
1 SE 07
1 4E O7
2 4E 10
J8EOS
NT
6 BE 10
T5E08
78E-10
S6E 13
37E 11
44E It
NT
62E 08
30E 11
43E 07
1 OE 10
42E 05
45E 11
NT
2 BE 05
4 3E 05
7 1E 05
TOTAL
MEAT &
EGG
NGESTION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E 04
49EO9
NT
5 3E 04
62E 08
6 IE 07
5 IE 07
8 BE 10
97E M
NT
8SE08
22E06
70E 09
82E If
36E 08
1 2E 08
NT
1 2E 05
30E 08
24E 05
7 4E 08
7 ?E 04
9 BE 10
NT
1 7E 03
76E 04
2 5E 03
Milk
Inqeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 04
2 BE 09
NT
46E 04
53E 08
28E 07
2 IE 07
3 BE 10
82E 04
NT
20E OB
1 4EO7
1 4E 08
15E 13
SSE 09
5 7E 09
NT
1 6E 05
50E 09
89E O5
1 4E 06
30E 05
54E 10
NT
1 4E 03
1 4( 04
1 6F 01
Chaese
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 SE OS
24E 10
NT
40E OS
46E 09
25E 08
1 9E 08
33E 11
71E-05
NT
1 BE 09
1 3E 08
1 3E 09
1 3E -1«
4 7E 10
50C 10
NT
1 4E 06
4 4E 10
7 7E 06
1 2E 07
2 6F 06
4 7F 11
W
1 IF 04
1 ?( 05
1 41 04
Milk
Desseils
Inqesliiin
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
t 9E 05
30E-10
NT
50E OS
5 BE 09
3 IE 08
2 3E 08
4 IE 11
89E-05
NT
2 2E-09
16E 08
1 6E 09
16E-H
59E 10
6 2E 10
NT
t 7E 06
54E 10
9 7E 06
1 5E 07
3 3E 06
59F 11
NT
1 6f 04
1 M 05
1 n 04
Yoguil
Inqoslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
S6E 06
90E 11
NT
1 SE OS
1 7E 09
92E 09
70E 09
1 2E 11
2 7E 05
NT
66E 10
4 7E 09
4 7E 10
4 BE IS
1 BE 10
I9F 10
NT
5 IE 07
1 6E 10
29E 06
4 5E 08
9»f n;
t flF 11
NT
4 n 05
4 4f 06
', ?l I)"")
Inqnslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 7E 06
60E 11
NT
IDE OS
1 2E 09
62E 09
46E 09
B2E 12
1 BE OS
NT
4 4E 10
32E 09
3 IE 10
32E 15
1 2E 10
1 2E 10
NT
34E 07
T IE TO
1 9f 06
3 OE 08
6 ">F 07
1 7\ 11
NT
1 If (IS
1 1)1 1)6
1 41 ()')
Biillm
logHSlion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
S6E O6
90E 11
NT
1 5E 05
1 7E 09
92E 09
70E 09
1 2E 11
2 7E 05
NT
66E 10
4 7E 09
4 7E 10
4 BE 15
1 BE 10
19E 10
NT
5 IE 07
1 6E 10
29F 06
4 5E 08
98f 07
1 Rf 11
NT
4 n OS
4 41 I*,
s ;i ()•>
     I V  A|l|KMldlI V IS
-------
        Avi| C.IMC i-i Ri'.k'. .mil Nun
                                    i'i HO',  Ailull Siilr
                                         NONCARCINOGFNIC HAZARD QUOTIENTS
           Chw?m at
2378 TCDD
12378 PeCOD
123478 H«CDO
123678 HuCDD
1 2 3 7 8,9 H«CDO
1.2.3.46.7.8 HpCDO
OCOO
2.3 78 TCDF
1.2 3 78PaCDF
234 78PeCDF
1 234 78H«CDF
1 236 78H»CDF
123789 H«CDF
23467 BHiCDF
1234678 H(>CDF
1.2.3.4 7 8.9 HpCDF
OCDF
He • achk>r i >6rpheny1
Heplachlofobrphenyl
B«n;o(a)pyrene
B«n;o(b)nuofanthane
Carbon lalrachloride
Diberu (a.h)arithi acene
Di(n)ocryt phlhalale
Haplachlor
Maiachloroben/ene
Maxachkxobuladiena
HaKacniofocyclopanladiene
HeiachkMophena
lndeno( 1.2,3-cd)pyr ena
Antimony
A/same
Barium
Beiyltium
Cadmium
Chromrum (haiavalenl)
Lead
Mnirui>
NK.knl
Sftlemum
Silver
T hallium
 IMOXIN 1EO
 ORGANICS  TOTAI  (mm ,|I,I.H.|
 INORGANICS  TOTAI
             SUBARF A TOTAI
Sllbdlfld
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El a.g
El avg
El a.g
El avg
El avg
El avg
El a.g
El avg
El avg
E1avg
El avg
Et avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
f. \ avg
Et avg
El avg
E 1 avg
E1 dvg
E 1 avq
El dvg
Et dvg
E 1 dvg
t \ dvq
TOTAL
DAIRY
PRODUCT
INGESTION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E 04
35E 09
NT
59E 04
6 BE 08
36E 07
2 7E 07
48E 10
1 OE 03
NT
26E 08
1 9E 07
1 8E 08
19E 13
70E 09
7 3E 09
NT
20E 05
6 4E 09
1 IE 04
1 BE 06
38E 05
69E 10
Nl
1 9E 03
1 7E 04
2 OE 03
Pnxluce
Ingestion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 OE 06
t BE O6
Nt
1 9E 08
1 4E 10
93E 09
1 6E 07
30E It
2 3E 07
NT
35E 08
25E 07
53E 09
9 7E 12
9 7E 08
2 7E 10
NT
1 OE 04
2 IE 09
4 4E 07
25E 08
6 4E 07
2 3F 08
NT
62E 06
1 OE 04
t IE 04
PiolRded
Pioduce
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 4E 12
t 5E 06
NT
1 4E 13
1 2E 12
76E 09
1 4E 07
25E 11
1 3E 09
NT
1 9E 08
82E 08
2 3E 09
1 3E 12
49E 08
8 3E 11
NT
86E 05
1 5E 09
2 BE 07
1 8E 08
26E 08
2 OE 08
NT
1 7E 06
86E 05
B 8F 05
Leafy
Piodure
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
88E OS
39E 07
NT
4 IE 07
30E 09
t IE 08
4 IE 08
20E 11
1 3E 07
NT
40E 08
2 3E 07
7 4E 09
69E 12
69E 08
1 4E 10
NT
1 3E 04
58E 10
1 4E 07
2 IE 08
36E 07
B 7E 09
NT
89E 05
t 3F 04
? 2E 04
Root
Piixiuce
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
49E 12
42E 07
NT
35E 09
7 IE 11
4 2E 07
5 IE 07
70E 10
1 3E-06
NT
44E 11
5 BE 11
40E 12
2 1E 16
1 7E 10
t OE 14
NT
32E 08
7 3E 14
79E 11
4 2E II
1 BE 12
5 8F 12
NT
2 7E 06
3 2E 08
? 7F 06
Exposed
Ft nil
Ingoslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
34E 06
1 5E U6
NT
16E 08
1 2E 10
79E 09
1 4E 07
26E 11
20E-07
NT
30E OB
2 IE 07
46E 09
83E 12
B 3E 08
23E 10
NT
87E 05
1 8E 09
38E 07
2 IE 08
54E 07
2 OE 08
NT
5 3F 06
8 BE 05
9 )F 05
Protected
Fruit
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E 12
36E 06
NT
34E 13
29E 12
18E 08
33E 07
60E-11
30E 09
NT
45E08
20E 07
S5E 09
30E 12
1 2E 07
20E 10
NT
2 1E 04
3 7E 09
6 7E 07
4 3E 08
62E 08
4 7E 08
NT
40E 06
2 IE 04
2 IE 04
TOTAL
FRUIT »
PRODUCE
INGESTION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
96E 05
93E 06
NT
45E 07
33E 09
48E 07
1 3E06
86E 10
1 9E 06
NT
1 7E 07
9 7E 07
25E 08
29E 11
4 IE 07
93E 10
NT
6 IE 04
9 7E 09
1 9E 06
1 3E 07
1 6E 06
1 2E 07
NT
1 IF 04
6 IE 04
7 2E 04
River
Walei
Ingnslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E 15
10E 12
NT
19E 16
t 5E 16
49E 13
23E 12
94E 16
1 3E 12
NT
3 BE 13
1 IE 11
97E 14
77E 16
29E 13
1 7E 14
NT
24E 10
20E 14
95E 12
1 IE 13
6 1E 11
1 IE 14
NT
5 1F 12
32F 10
3 ?F 10
Rivor
Walm
Dermal
Contact
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E 11
23E 11
NT
52E 12
24E 13
8 IE-ID
7 7E 10
74E 13
1 3E 08
NT
14E 13
40E 12
35E 14
2 BE 16
1 IE 13
62E 15
NT
86E It
7 2E 15
35E 12
39E 14
2 2E 11
48F 15
NT
1 51 08
i n to
1 •>( 08
Lakn
Water
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
NA
NA
MA
NA
MA
Wdlpr
Diurnal
Conlai 1
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
MA
MA
HA
MA
MA
MA
MA
NA
TOTAL
HI
NT
NT
NT
NT
NT
NT
Ni
NT
NT
NT
Nt
NT
NT
NT
NT
NT
NT
NT
NT
NT
Nl
NT
5 IE 04
93E 06
NT
1 IE 03
1 3E 07
1 5E 06
2 7E 06
25E 09
20E OJ
NT
29E 07
3 7E 06
5 3E 08
1 7F 10
461 07
2 2F 08
NT
ssr 04
4 fit OH
T 4F 04
2 Of 06
7 n 04
i ?r oc
m
1 7f 0 )
1  n n i
-------
                  * %
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                                                                                                           n
-------
M.tx C.iftc«*i Risks .tint Ntift( ,«n< m MCK  Adult Suhsisd
                                    NONCARCINOGENIC HA/ARO QUOTIENTS
1
Chemical
2.3 7 8 TCDD
1.2 3 7BP»CDD
1.2.34.78 HxCDD
1.2.3.6.78 HxCDD
1.2.3. 7.8.9 HxCDD
1.2.3.4,6.7.8 HpCDO
OCOD
2.3.7.8 TCDF
1.2 3.78 PeCDF
2 3.4 7.8 PeCDF
1 2.3.4 7 8 HxCDF
1 2.3.6.7.8 HxCDF
12 3.7 8 9 HxCDF
2.3.4 6 7.8 HxCDF
1 2.3 4.6 7 8 HpCDF
1.2 3,4.7.8.9 HpCDF
OCDF
Tatfachlorobfphenyf
Hexachfofobrphenyl
Heptachforobiphenyl
Ben/o(a)pyien0
Beruo(b)fluoi anlhene
Carbon lehachlwide
Diheru (a.h)anlhi scene
Di(n)oclyt phlhalato
Heptachloi
H0xachloiob»n;0n«
Hexachlmobutadrerw
Hexachkxocyclopanladrene
Hexacnlnropfcene
lnderio(l,2,3 cdlpyiene
Antimony
Arsenic ~'
Barium
Beryllium
Cadmium
Chromrum (heiavalenl)
lead
Mercury
Nil k»l
Splefntim
Silver
Tin Ilium
?,,,r
OIOXIN IEQ
ORGANICS TOTAl (mm ilinun)
INORGANICS TOT At
SUBAREA TOTAl
Suhaiea
f 1 max
i t max
E 1 max
E 1 max
Et max
El max
Et max
Et max
Et max
Et max
El max
Et max
El max
El max
E 1 max
E 1 max
E 1 max
E t max
E 1 max
E 1 max
E 1 max
El max
E 1 max
El max
El max
El max
El max
Et max
El max
El max
Et max
Et max
Et max
El max
El max
El max
El max
E 1 max
E 1 max
E 1 max
E 1 rnax
E t max
E 1 max
E 1 ma«
Et n.a.
E t max
El inj>
Et max
E 1 rn.ii
Soil
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 3E 10
60E-08
NT
89E It
70E 11
84E OS
92E 07
43E tO
2 2E 07
NT
t IE 08
29E 09
86E 11
48E 09
2 3E 09
NT
1 IE 05
8 3E 10
6 IE 07
30E 09
1 IE 05
36E 10
NT
1 3E 06
2 3E 05
2 5E 05
Soil
Dermal
Contact
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E 10
85E 08
NT
97E 11
7 7E 11
92E 08
10E06
4 7E 10
24E 07
NT
1 9E 09
98E 08
52E 10
1 6E 11
86E 10
4 IE !0
NT
2 IE 06
1 5E 10
1 IE 07
5 4E 10
20E 06
65E 11
NT
1 4E 06
4 2E 06
5 7E 06
Beef
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E 04
8 BE 0/9
NT
1 6E 03
1 9E 07
1 IE 06
86E 07
1 5E 09
1 8E 03
NT
1 3E 07
3 IE 06
39E 09
1 IE 10
55E 08
1 4E 08
NT
1 4E 05
1 9E 08
38E 06
1 3E 07
40E 04
1 3E 09
NT
40E 03
4 2E 04
4 4E 03
Pork
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
t 4E 09
NT
4 4E 05
5 SEW
32E-07
296 07
50E 10
4 3E-05
NT
2 1E-08
40E 07
70E-09
32E 11
1 OE-09
64E49
NT
1 9E 05
3 2E 08
35E 05
1 2E 09
56E 04
1 4E 10
NT
1 OE 04
6 2E 04
72E 04
Chicken
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
55E 13
89E 12
NT
1 2E 10
1 5E 12
82E 10
78E 10
1 3E 12
9 IE 08
NT
22E 10
37E 12
1 BE 12
5 BE 09
1 OE 10
NT
50E 06
70E 11
t 6E 06
1 9E 11
1 6E 04
1 7E 10
NT
9 3E 08
1 6E 04
1 6F 04
Other
Poultry
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 5E 13
24E 12
NT
32E 11
4 1E-I3
2 2E to
2 IE 10
35E 13
25E-08
NT
59E 11
5 BE 08
99E 13
48E 13
t 6E 09
2 BE 11
NT
1 4E 06
1 9E 11
44E 07
5 2E 12
4 3E 05
45E 11
NT
2 5E 08
4 4E 05
4 4F OS
Egg
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 IE 10
5 1E-09
NT
89E 08
8 7E tO
4 7E 07
4 5E-07
74E 10
S2E-05
NT
1 2E 09
1 3E 07
1 3E 09
95E 13
83E 11
78E It
NT
1 96 07
52E 11
7 4E 07
1 8E 10
7 2E 05
76E 11
NT
53E 05
7 3E 05
t 3E 04
TOTAL
MEAT &
EGG
INGEST ION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
62E 04
NT
t 7E 03
t 9E-07
19E06
1 66 08
2 BE 09
1 9E-03
NT
1 5E 07
39E06
1 2E 08
t 4E 10
63E 08
2 t£48
NT
39EOS
5 IE 08
4 2E 05
1 3E 07
1 2E 03
1 7E 09
NT
4 IE 03
1 3E 03
55E 03
Milk
tngestron
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
53E44
87E09
NT
1 4E 03
1 7E 07
89E-07
6 7E 07
1 2E 09
1 6E 03
NT
36E46
26E 07
26E 08
2 BE 13
97E 09
10EOB
NT
50E 05
89E 09
1 6E 04
25E 06
52E 05
94E 10
NT
35E 03
26E 04
3 8F 01
Cheese
Inqeslroi)
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
46E 05
75E tO
NT
1 3E 04
14E08
7 7E 08
S BE 08
1 OE tO
1 4E-04
NT
3 IE 09
22E 08
22E 14
84E 10
8 7E 10
NT
4 3E 06
7 7E 10
1 4E 05
2 1E 07
46E 06
82E 11
NT
3 If 04
? if m
i if o<
Milk
Desserts
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
58E OS
94E 10
NT
16E04
t BE 08
9 7E 08
7 3E 08
1 3E 10
t /E 04
NT
39E 09
2 BE 08
2 BE 09
2 BE 14
t IE 09
t IE 09
NT
54E 06
96E 10
1 7E 05
2 7E 07
5 7E 06
1 OE 10
NT
39F 04
28f 05
4 If 04
Yi>gur!
Irignslnm
HQ
NT
N1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 05
28E 10
NT
4 7E OS
54E 09
29E OB
22E 08
3 BE 11
5 IE -05
NT
1 2E 09
84E 09
BSE 10
84E 15
32E 10
33E 10
NT
16E 06
29E 10
5 IE 06
8 OF OB
1 n 06
1 IF 11

1 ?f 04
0 rif Of,
t 7f (14
CrfMrn
Inqristrori
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
KIT
f"t r
NT
1 2E 05
t 9E 10
NT
3 IE 05
36E 09
t 9E 08
15E 08
26E 11
34E 05
NT
7 BE 10
56E 09
56E 10
56E 15
2 IE 10
2 2E 10
N1
1 1E 06
1 9F 10
J 4f 06
5 if OB
t If 06
2 Of It
f ( I
ri f
i rr 05
'> 7f 06
B II OS
Buller
Ingnslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
KIT
M 1
NT

NT

NT
t 7E 05
2 BE 10
NT
4 7E 05
54E 09
29E 08
22E OB
3 BE 11
5 IE 05
fj T
f» r
1 2E 09
84E 09
8 3E 10
84E 15
32E 10
3 3F 10
NT
16F 06
29E 10
5 IF 06
8 OF 08
3 IF II

1 2F 04
8M 06
1 ;i 04
-------
          M.IK C.mri'1 Ri'.ks .mil Nu
                                        i HO. Ad,ill SiiliM-.l.tm c f .ill
                                         NONCARCINOGENIC HAZARD QUOTIENTS
           Chemical
? 3 78 TCI
I 2.3 78 PnCDD
t 234 78HxCDO
1.2.36 78 HxCDD
123 789 HxCDD
t.2.3.4 6.7.8 HpCDO
DC DO
?.3 7.8 TCDF
1.2 3.78 PeC OF
? 3.4 7SPeCDF
I 2.3.4.7.8 HxCDF
17 36 78 HxCDF
12 3 789H.CDF
' 34678H«CDF
1234678 HpCDF
1.2 3.4 7.8.9 HpCDF
DCDF
f el i ac hloi obiphenyl
 leiachlorobiplteny!
 Hepl ac hloiobipbanyl
Jan/o(a)pyiane
 toruo(b)fluoianflM)ne
 ht(2 athyttMiytyphlnalate
 :aibon laliachkMida
 )i(n>oclyt phlhalala
 1aptachlo>
 taxachloiobaruana
 laxachlmobuladiana
 laxachlotocyclopanladiene
 texacnlofophena
 mlimony
 usenic
 laiium
 tarytiium
 ladmium
 'niomium (hexavalenl)

 Inicury
 hrkal
 .Blumum
  itvm
  h.illium
 D JX.IN TEQ
 ORGANICS TOTAL (mm dm.in)
 INORGANICS TOTAL
              SUBAREA TOTAL
Subaiea
E 1 max
E 1 max
E 1 man
El man
E 1 max
El mai
El max
E 1 max
El max
61 max
E 1 max
El max
E 1 max
El max
El max
E 1 max
E 1 max
E 1 max
E t max
E 1 max
E1 max
El max
E 1 max
E 1 max
E 1 max
El max
E t max
El max
El max
El max
Et max
61 max
Et max
Et max
El max
E t max
El max
E 1 max
E 1 max
E 1 max
E mai
E max
E max
E max
t ma.
E max
E nidi
E ma.
E 1 in.i-
TOTAL
DAIRY
PRODUCT
INGEST ION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
696 04
1 IE 08
NT
1 BE 03
2 IE 07
1 IE 06
866 07
1 SE 09
20E 03
NT
466 08
336 07
336 08
33E 13
t 2EO8
1 3E 08
NT
64E 05
1 1E 08
20E 04
12E 06
6 7E 05
1 2E 09
NT
45E 03
3 4E 04
49E 03
Pioduce
Ingnslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 05
56E 06
NT
59E 08
4 3E 10
29E 08
50E 07
94E 11
45E07
NT
6 IE 08
44E 07
93E 09
1 76 11
1 76 07
48E 10
NT
3 2E 04
3 7E 09
7 7E 07
4 2E 08
1 IE 06
4 OE OB
NT
1 9E 05
3 2E 04
3 4E 04
Piolected
Pioduce
Inpeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
32E 12
4 BE 06
NT
45E 13
39E 12
2 4E 08
43E 07
79E 11
2 4E 09
NT
32E 08
1 4E 07
39E 09
2 2E 12
B 4E 08
1 4E 10
NT
2 7E 04
26E 09
4 BE 07
JOE 08
4 4E 08
34E 08
NT
52E 06
2 7E 04
2 8E 04
leafy
Pioduce
digestion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 BE 04
1 2E 06
NT
1 IE 06
94E 09
33E 08
1 3E 07
646 11
2 6E 07
NT
69E 08
40E 07
1 3E 08
1 2E tt
1 2E 07
2 4E 10
NT
406 04
t OE 09
24E 07
35E 08
64E 07
1 5E 08
NT
2 BE 04
4 IE 04
69E 04
Root
Pioduce
Ingeslinn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 11
1 36-06
NT
1 16 08
226 10
1 36 06
1 86 06
226 09
24606
NT
766 11
996 11
696 12
366 16
296 10
t 86 14
NT
1 06 07
1 3E 13
1 4E 10
72E 11
3 IE 12
99E 12
NT
6 7E 06
1 OE 07
6 BE 06
E x posed
Fiuil
liigeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE-OS
4BEO6
NT
50E 08
3 7E 10
25E08
4 3E07
8 IE 11
3BE07
NT
52EO8
3 7E 07
806 09
1 5E 11
14E07
4 IE 10
NT
2 7E 04
3 IE 09
6SE 07
36E 08
9 7E 07
3 4E 08
NT
1 6E 05
2 7E 04
2 9E 04
Piolecled
Fiuil
Ingnslhin
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
766 12
1 IE 05
NT
1 IE 12
92E 12
57E 08
106 06
196 10
576-09
NT
776 08
33E 07
94609
S2E 12
206 07
346 10
NT
646 04
6 36 09
1 IE 06
7 3E 08
1 IE 07
8 IE -08
NT
1 3E 05
65E 04
66E 04
TOTAL
FRUIT &
PRODUCE
INGESTION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30604
29E-05
NT
1 46 06
10608
156 06
4 IE 06
27E09
356 06
NT
29E 07
1 76 06
43E 08
526 11
72E 07
16E09
NT
19E 03
1 7E 08
33E 06
2 2E 07
29E 06
20E 07
NT
34E 04
1 9E 03
2 3E 03
Rivm
Walei
liigeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
64E 15
2 76 12
NT
5 16 16
396 16
1 36 12
62E 12
256 15
2 36-12
NT
636 13
1 BE 11
16E 13
1 36 15
486 13
28E 14
NT
63E 10
33E 14
1 6E 11
1 8E 13
1 OE 10
2 2E 14
NT
1 2E 11
7 7E 10
7 BF 10
Rivei
W.ilni
Conlacl
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
506-11
63E-11
NT
1 4E It
63E 13
22E09
2 16 09
206 12
246-08
NT
236 13
666-12
586 14
466 16
1 76 13
1 OE 14
NT
23E 10
1 2E 14
5 7E 12
65E 14
3 7E 11
79E 15
NT
2 8F 08
2BF 10
? 81 Ofl
Wdloi
Ingfistion
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
flA
NA
NA
lake
W.il.-i
Dnnn,il
Conlacl
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
MA
TOTAL
HI
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
16E 03
29E 05
NT
35E 03
42E 07
47E 06
BSE 06
79E 09
39E 03
NT
50E 07
66E 06
92E 08
30E 10
80E 07
3 BE 08
Nl
20t 01
8 IE 08
25f 04
3Sf 06
1 If Q)
? If 07
Nl
901 HI
16f 03
1 If 07
 i.lllinr V A|i|M-llfll> V 15

                      c
-------
                           APPENDIX V-16




              Exposure Pathway Cancer Risks and Hazard Indices
Volume V
-------
TABLE 1
Average Cancer Risks for an Adult Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meal &
F-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Uke
Ingestion
Uke
Dermal
Contact
Total
Risk
Subarea
El
1 x 10 '"
6 x 10"
5 x 10"
8 x 10*
6 x 10"
2 x 10"
7 x I0'!
v NA
NA
I x 10 7
E2
4 x 10"
2 x 10"
2 x 10s
4 x 10"
3 x 10"
6 x 10"
2 x 10"
NA
NA
6 x 10"
E3
2 x 10"
9 x IO'2
1 x 10s
2 x 10*
1 x 10"
2 x 10"
7 x IO11
NA
NA
3 x 10"
Nl
6 x 10"
3 x 10"
2 x 10*
4 x 10*
3 x 10"
NA
NA
NA
NA
6 x 10*
N2
2 x 10"
1 x 10"
9 x 10"
2 x 10"
1 x 10'
3 x 10"
3 x 10 '•
NA
NA
3 x 10"
N3
1 x 10"
5 x IO12
4 x 10"
7 x 10'
5 x 10"'
NA
NA
NA
NA
1 x 10*
SI
5 x 10"
2 x 10"
2 x 10"
4 x 10"
3 x 10'
2 x 10"
9 x 10"
NA
NA
6 x 10*
S2
2 x 10"
8 x 10 l2
1 x 10"
2 x 10*
1 x 10'
NA
NA
NA
NA
3 x 10*
S3
7 x IO12
4 x IO12
5 x 10'
8 x 10'
6 x 10'"
NA
NA
3 x 10"
2 x IO12
1 x 10"
Wl
7 x 10"
3 x 10"
3 x 10"
5 x 10*
4 x 10'
NA
NA
NA
NA
9 x 10"
W2
3 x 10"
1 x 10"
2 x 10"
3 x 10*
2 x 10'
3 x 10 n
1 x 10"
NA
NA
4 x 10"
W3
1 x 10"
6 x 10 l2
7 x 10'
1 x 10*
9 x 10 "'
3 x 10"
1 x 10"
NA
NA
2 x 10"
Volume V
Appendix V-16
-------
TABLE 2
Average Cancer Risks for a Child Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Fgg
Ingestion
Dairy
Ingestion
Vegetable
& Fmit
Ingestion
River
Ingestion
River
Dermal
Contact
l,ake
Ingestion
l,ake
Dermal
Contact
Total
Risk
Subarea
El
2 x 10'
1 x 10 ln
5 x 10"
3 x 10 7
7 x 10"
o x 10"
9 x 10 |:
NA
x,
NA
3 x 10'
E2
6 x 10'°
3 x 10"
3 x 10"
1 x 10'
4 x 10"
2 x 10"
3 x tO'2
NA
NA
2 x I07
E3
2 x 10 '"
1 x 10"
1 x 10*
6 x 10"
2 \ 10"
6 x 10"
9 x I0n
NA
NA
7 x 10*
Nl
8 x 10 ">
5 x 10"
3 x 10"
1 x 10'
4 x 10"
NA
NA
NA
NA
2 x 10'
N2
3 x 10 in
2 x 10"
1 x 10"
5 x 10s
t x 10'
9 x 10"
4 x IO'2
NA
NA
6 x 10s
N3
1 x 10'°
1 x 1012
4 x 10"
2 x 10s
6 x 10 lfl
NA
NA
NA
NA
3 x 10s
SI
6 x 10 10
4 x 10"
3 x 10*
1 x I07
4 x 10'
7 x 10"
1 x 10"
NA
NA
2 x I07
S2
2 x 10'"
1 x 10"
1 x 10"
6 x 10"
2x 10'
NA
NA
NA
NA
7 x ID"
S3
9 x 10"
6 x I012
5 x 10'
3 x 10*
7 x 10 m
NA
NA
1 x 10"
2 x 10"
3 x 10"
Wl
9 x 10'°
5 x 10"
4 x 10"
2 x I07
5 x 10'
NA
NA
NA
NA
2 x 10 '
\V2
3 x 10 10
2 x 10"
2 x 10"
9 x 10s
2 x 10'
8 x 10"
1 x 10"
NA
NA
1 x 10'
W3
2 x 10 '"
9 x IOP
8 x 10"
4 x 10s
1 x 10'
8 x 10"
1 x 10"
NA
NA
"5 x 10"
Volume V
Appendix V-16
         I
-------

Kxposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Rgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
[.ake
Ingestion
Lake
Dermal
Contact
.
Total
Risk
TABLE 3
Average Cancer Risks for a School-age Child

El
2 x 10 '"
6 x 10"
5 x 10"
2 x I07
5 x 10"
3 x 10"
6 x IO|:
NA
NA
•••
2 x It)7

E2
8 x 10"
? x 10"
2 x 10"
8 x 10*
3 x 10"
9 x 10 "
2 x IO'2
NA
NA
1 x I07

E3
3 x 10"
1 x 10"
1 x 10"
3 x 10"
1 x 10"
3 x 10"
6 x 1011
NA
NA
=====
4 x 10*

Nl
1 x 10 ln
3 x 10"
2 x 10"
8 x 10"
3 x l()g
NA
NA
NA
NA
1 x 10 7
S u h area
N2
4 x 10"
1 x 10"
1 x 10*
3 x 10*
1 x IO9
4 x 10"
3 x 10 l2
NA
NA
4 x 10s
N3
2 x 10"
5 x IO12
4 x 10"
1 x 10"
5 x 10'"
NA
NA
NA
NA
= ' 	 	
2 x 10*
SI
9 x 10"
3 x 10"
2 x 10"
8 x 10"
3 x 10'
3 x 10"
8 x IO'2
NA
NA
1 x 10 7
S2
3 x 10"
8 x IO12
1 x 10"
4 x 10"
1 x 10"
NA
NA
NA
NA
5 x 10"
S3
1 x 10"
4 x I012
5 x 10'
2 x 10*
5 x 10 I0
NA
NA
5 x 10"
2 x I017
	 " 	 ~ _. -
2 x 10*

Wl
1 x 10'°
4 x 10"
3 x 10"
1 x I07
4 x !()'
NA
NA
NA
NA
1 x H)7

W2
5 x 10"
1 x 10"
2 x 10*
5 x 10*
2 x I09
4 x 10"
8 x 10 l2
NA
NA
7 x 10"

W3
2 x 10"
6 x IO'2
7 x 10 '
2 x 10*
8 x 10 '"
4 x 10"
9 x 10 '2
NA
NA
1 x 10"

Volume V
Appendix V-16
-------
TAKLE 4
Average Cancer Risks for an Adult Fanner
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Egg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
l>ake
Ingestion
Uke
Dermal
Contact
Total
Risk
Subarea
El
7 x 10'°
4 x 10'°
3 x 10 7
2 x 10 7
1 x 10"
4 x 10"
2 x 10"
NA
>•
NA
5 x 10 7
E2
2 x 10'°
1 x 10 '"
1 x 107
1 x 10 7
6 x 10'
1 x 10"
5 x 10 n
NA
NA
3 x 107
E3
1 x 10 '"
6 x 10"
6 x 10"
5 x 10"
3 x 10"
4 x 10"
2 x I012
NA
NA
1 x I07
Nt
4 x H)ln
2 x 10 in
1 x I07
1 x 10 7
6 x 10'
NA
NA
NA
NA
3 x 10 7
N2
1 x 10'°
7 x 10"
6 x 10"
4 x 10*
2 x 10"
6 x 10"
7 x 10"
NA
NA
1 x l()7
N3
5 x 10"
3 x 10"
3 x 10"
2 x 10s
1 x 10"
NA
NA
NA
NA
4 x 10"
SI
3 x 10'°
2 x 10 '"
1 x 107
1 x 107
6 x 10"
5 x 10"
2 x 10"
NA
NA
3 x H)7
S2
9 x 10"
5 x 10"
7 x 10*
5 x 10"
3 x 10'
NA
NA
NA
NA
1 x H)7
S3
4 x 10"
2 x 10"
3 x 10"
2 x 10"
1 x 10'
NA
NA
8 x 10"
4 x 10"
5 x 10"
Wl
4 x 10'°
2 x 10 "'
2 x I07
2 x I07
9 x 10'
NA
NA
NA
NA
4 x H)7
W2
1 x 10'°
8 x 10"
1 x 107
7 x 10"
4 x 10"
6 x 10"
2 x 10"
NA
NA
2 x H)7
\V3
7 x 10"
4 x 10"
5 x 10"
3 x 10"
2 x 10"
6 x 10"
2 x 10"
NA
NA
8 x 10"
Volume V
Appendix V-16
-------
TABLE 5
Average Cancer Risks for :i Fanner Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meal &
Pgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Subarea
E!
2 x 10"
1 x 10 I0
2 x 107
1 x 10'
7 x 10'
6 x 10"
9 x 10 l2
NA
NA
5 x 10 7
E2
6 x 10'°
3 x 10"
7 x 10"
2 x 10'
4 x 10"
2 x 10"
3 x IO12
NA
NA
2 x 107
E3
2 x 10 '"
1 x 10"
3 x 10"
7 x 10*
2 x 10'
6 x 10 '«
9 x IO11
NA
NA
1 x 10'
Nl
8 x IO"1
5 x 10"
7 x 10"
2 x 10'
4 x 10'
NA
NA
NA
NA
2 x IO7
N2
3 x 10 ln
2 x 10"
3 x 10*
6 x 10*
1 x 10'
9 x 10"
4 x 10 '2
NA
NA
9 x 10*
N3
1 x 10 I0
7 x IO'2
1 x 10*
3 x 10*
6 x 10 '"
NA
NA
NA
NA
4 x 10*
$1
6 x 10'°
4 x 10"
7 x IO8
2 x IO7
4 x 10'
7 x 10-"
1 x 10"
NA
NA
2 x 10 7
S2
2 x 10'°
1 x 10"
3 x 10"
7 x 10"
2 x 10'
NA
NA
NA
NA
1 x IO7
S3
9 x 10"
6 x IO'2
1 x IO8
3 x IO8
7 x IO10
NA
NA
1 x IO14
2 x 10"
5 x 10"
W1
9 x 10 ln
5 x 10"
1 x IO7
2 x IO7
5 x 10'
NA
NA
NA
NA
} x IO7
VV2
3 x 10 '"
2 x 10"
5 x 10 8
1 x IO7
2 x I0g
8 x 10"
1 x 10"
NA
NA
2 x 10'
VV3
2 x 10 ln
9 x 10 "
2 x 10"
5 x 10*
1 x 10"
8 x 10"
1 x 10"
NA
NA
7 x 10"
Volume V
Appendix V-16
-------
TABLE 6
Average Cancer Risks For an Adult Subsistence Fanner
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
f;-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Uke
Dermal
Contact
Total
Risk
Stibarea
El
7 x 10 '"
4 x 10'°
7 x 10'
6 x 10'
5 x 10"
4 x 10"
2 x 10"
NA
x,
NA
1 x 10 6
E2
2 x 10 in
1 x 10 I0
3 x 10 7
3 x 10'
2 x 10"
1 x 10"
5 x IO'2
NA
NA
6 x IO1
E3
1 x IO10
6 x 10"
1 x 10'
I x 10'
1 x 10"
4 x 10"
2 x IO12
NA
NA
3 x IO7
Nl
4 x 10'"
2 x If)"1
3 x 10'
1 x 10'
2 x 10"
NA
NA
NA
NA
6 x If)7
N2
1 x If)10
7 x 10"
1 x IO7
1 x IO7
1 x 10*
6 x 10"
7 x IO12
NA
NA
2 x 10'
N3
5 x 10"
3 x 10"
6 x 10s
5 x 10"
4 x 10'
NA
NA
NA
NA
1 x IO7
SI
3 x If)10
2 x 10 I0
3 x IO7
3 x IO7
2 x 10"
5 x 10"
2 x 10"
NA
NA
6 x If)7
S2
9 x 10"
5 x 10"
2 x IO7
1 x IO7
1 x 10s
NA
NA
NA
NA
3 x 10'
S3
4 x 10"
2 x 10"
7 x 10"
5 x IO8
5 x 10'
NA
NA
8 x 10"
4 x 10I?
1 x IO7
YV1
4 x IO"1
2 x If)"1
5 x IO7
4 x IO7
4 x 10"
NA
NA
NA
NA
9 x If)7
W2
1 x If)10
8 x 10"
2 x IO7
2 x IO7
2 x 10"
6 x 10"
2 x 10"
NA
NA
4 x 10'
W3
7 x 10"
4 x 10"
1 x IO7
8 x 10"
8 x 10"
6 x 10"
2 x 10"
NA
NA
2 x 10'
Volume V
Appendix V-16
-------
TABLE 7
Average Cancer Risks for a Subsistence Fanner Child
Exposure
Pathway
Soil
Ingeslion
Soil
Dermal
Contact
Meat &
':-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Subarea
El
2 x It)9
1 x 10 ln
3 x 10 7
9 x 10'
3 x 10"
6 x 10"
9 x I012
NA
NA
1 x 10"
E2
6 x 10 I0
3 x 10"
2 x I07
4 x 10 7
2 x 10"
2 x 10"
3 x 10'2
NA
NA
6 x 107
E3
2 x 10'°
1 x 10"
7 x 10"
2 x 10'
6 x 10'
6 x 10"
9 x 1011
NA
NA
2 x 10'
Nl
8 x 10 '"
5 x 10"
2 X 10'
4 x 10'
2 x 10"
NA
NA
NA
NA
6 x 10'
N2
3 x 10 '"
2 x 10"
7 x 10"
2 x 10'
6 x 10'
9 x 10"
4 x 10 '2
NA
NA
2 x 10'
N3
1 x 10"'
7 x 1012
3 x 10"
7 x 10"
3 x 10"
NA
NA
NA
NA
1 x 10 7
SI
6 x 10 "'
4 x 10"
2 x 10 7
4 x 107
2 x 10"
7 x 10"
1 x 10"
NA
NA
6 x It)7
S2
2 x 10'°
1 x 10"
8 x 10"
2 x I07
7 x 10'
NA
NA
NA
NA
3 x 10'
S3
9 x 10"
6 x 10"
3 x 10"
8 x 10"
3 x 10'
NA
NA
1 x 10 l4
2 x 10 n
1 x 10'
VVI
9 x 10 10
5 x 10"
2 x 10 7
6 x 107
2 x 10"
NA
NA
NA
NA
8 x 10'

W2
3 x 10 '"
2 x 10"
1 x 107
3 x I07
1 x 10"
8 x 10"
1 x 10"
NA
NA
4 x 10'

VV3 |
2x 10'"
9 x 10 l?
5 x 10"
1 x I07
5 x 10"
8 x 10"
1 x 10"
NA
NA
2 x 10'
Volume V
Appendix V-16
-------
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-------
TABLE 9
Average Noncancrr Hazard Indices Tor a Child Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Kgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
III
Suharea
El
8 x 10s
2 x 10"
6 x 10"
4 x 10 '
4 x 10 4
2 x 10'
3 x 10"
NA
NA
5 x 10'
E2
3 x 10s
7 x I07
2 x 10"
2 x 10'
2 x I04
6 x 10 10
1 x 10"
NA
NA
2 x 10'
E3
1 x 10s
3 x 10'
9 x 10'
7 x 10"
8 x 10s
2 x 10 10
3 x 10"
NA
NA
8 x 10 4
Nl
4 x 10'
1 x 10*
3 x 10 4
2 x 10'
2 x 10"
NA
NA
NA
NA
3 x 10'
N2
1 x 10s
3 x 10'
1 x I04
7 x I04
8 x 10'
5 x 10"
5 x 10*
NA
NA "
9 x I04
N3
7 x 10*
2 x 107
5 x 10'
3 x 1()4
3 x 10'
NA
NA
NA
NA
4 x 104
SI
3 x 10'
8 x 10 7
2 x 104
2 x 101
2 x 10"
2 x 10'
3 x 10"
NA
NA
2 x 10'
S2
1 x 10'
3 x I07
7 x 10'
6 x 10"
9x 10'
NA
NA
NA
NA
8 x 10"
S3
5 x 10*
1 x 10 '
3 x 10'
3 x 10"
4 x 10'
NA
NA
9 x 10"
8 x 10"
3 x 10'
VVI
5 x 10'
1 x 10*
3 x 10^
2 x 10 1
3 x 10"
NA
NA
NA
NA
3 x 10'
W2
2 x 10'
5 x 10 7
1 x I04
9 x 10 <
1 x l()4
2 x 10'
4 x 10"
NA
NA
1 x 10'
W3
9 x 10"
2 x 10'
6 x 10'
4 x 10 4
6 x 10'
2 x 10'
4 x 10"
NA
NA
6 x 10 1
Volume V
Appendix V-16
-------
TARI.E 10
Average Noncancer Hazard Indices for a School-age Child
Exposure
F'alhvvay
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Fgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
HI
Suharea
El
1 x 10'
1 x 10*
5 x 10"
2 x 10'
3 x 10"
7 x 10 In
2 x 10"
NA
V
NA
3 x 10'
E2
4 x 10-6
5 x 107
2 x 10"
8 x 10"
1 x 10"
3 x 10 ln
7 x 10"
NA
NA
1 x 10 '
E3
2 x 10*
2 x 10'
8 x 10s
3 x \(}4
5 x 10'
9 x 10"
2 x 10'
NA
NA
5 x IOJ
Nl
6 x 10"
6 x I07
2 x IOJ
1 x H)1
1 x 10 4
NA
NA
NA
NA
1 x 10'
N2
2 x 10*
2 x 107
8 x 10'
4 x lO4
5 x 10'
2 x 10"
4 x 10"
NA
NA
5 x 10"
N3
1 x I06
1 x I07
5 x 10'
2 x 10"
2 x 10'
NA
NA
NA
NA
2 x )()<
SI
5 x 10'
5 x 107
2 x 10"
9 x 104
1 x 10"
9 x 10 I0
2 x 10"
NA
NA
1 x 10 1
S2
2 x 10*
2 x 107
6 x 10'
3 x 10"
6 x 10'
NA
NA
NA
NA
4 x 10"
S3
8x I07
9 x 10"
3 x 10'
I x 10"
3 x 10'
NA
NA
4 x 10"
6 x 10"
2 x H)4
Wl
7 x 10*
8 x I07
3 x 10"
I x I01
2 x 10"
NA
NA
NA
NA
2 x If)1
VV2
3 x I06
3 x 107
1 x 10"
5 x IOJ
9 x 10'
1 x 10'
3 x 10"
NA
NA
7 x I01
W3
1 x 10*
1 x K)7
5 x 10'
2 x 10 4
4 x 10'
1 x 10"
3 x 10"
NA
NA
} x I01
Volume V
Appendix  V 16
10
-------
TABLF II
Average Noncancer Hazard Indices for an Adult Fanner
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
F-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
III
Suharea
El
1 x 10'
2 x KT6
9 x 10"
6 x 10"
1 x 10"
3 x 10'°
2 x 108
NA
*.
NA
2 x 10'
E2
4 x 10-*
9 x 10'
3 x 10"
2 x 10"
7 x 10'
1 x 10'°
5 x 10'
NA
NA
6 x K)4
E3
2 x 10*
4 x I07
1 x I04
1 x 10"
3 x 1C)'
4 x 10"
2 x I09
NA
NA
3 x 10"
Nl
6 x 10*
I x 10*
5 x 10"
3 x 10"
7 x 10'
NA
NA
NA
NA
8 x 10 J
N2
2 x 10*
4 x I07
2 x 10"
1 x 10"
3 x 10'
1 x 10'
3 x 10*
NA
NA
3 x 10"
N3
9 x 107
2 x 107
7 x 10'
5 x 10'
1 x 10'
NA
NA
NA
NA
1 x 10"
SI
5 x 10*
1 x I06
4 x 10"
3 x 10"
7 x 105
4 x 10'°
2 x 10"
NA
NA
7 x 10"
S2
2 x I06
4 x 107
1 x 10"
9 x 10'
3 x I05
NA
NA
NA
NA
2 x 10 •'
S3
7 x 107
2 x I07
5 x 10'
4 x 10'
1 x 10s
NA
NA
2 x 10'
4 x 10"
1 x 10 •'
Wl
6 x 10*
1 x 10*
5 x 10"
4 x 10"
1 x 10"
NA
NA
NA
NA
1 x K)1
W2
3 x 10*
6 x 10 7
2 x 10"
1 x 10 4
5 x 10'
5 x 10 ln
2 x 10"
NA
NA
4 x K)1
VV3
1 x If)6
3 x 10 7
9 x 10'
6 x K)'
2 x 10'
5 x 10 '"
2 x 10"
NA
NA
2 x 10"
Volume  V
Appendix V-16
-------
TABU: 12
Average Noncanccr Hazard Indices for a Fanner Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
F-gg
Ingestion
Dairy
Ingestion
Vegetable
& Pruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Uke
Dermal
Contact
Total
III
Sufoarea
El
8 x 10'
2 x 10*
2 x I01
5 x 10'
4 x 10"
2 x 10"
3 x 10s
NA
NA
8 x 10'
E2
3 x 10s
7 x 10?
6 x 10"
2 x 10'
2 x K)4
6 x 10'"
1 x 10*
NA
NA
3 x I01
E3
1 x 10'
3 x 10 7
3 x 10"
8 x 10"
8 x 10'
2 x 10 I0
3 x 10"
NA
NA
1 x 10'
Nl
4 x 10'
1 x 10*
9 x 10"
3 x 10 '
2 r IOJ
NA
NA
NA
NA
4 x 10'
N2
1 x 10'
3 x 10'
3 x 10"
9 x 10"
8 x 10'
5 x 10'
5 x 10"
NA
NA
1 x 10'
N3
7 x I06
2 x 107
1 x 10"
4 x 10"
3 x 10'
NA
NA
NA
NA
6 x 10"
SI
3 x 10'
8 x 10'
7 x 10"
2 x I01
2 x 10"
2 x 10'
3 x 10"
NA
NA
3 x 10 '
S2
1 x 10'
3 x 107
2 x 10"
7 x 10"
9 x 10'
NA
NA
NA
NA
1 x 101
S3
5 x 10"
1 x 107
1 x 10^
3 x 10"
4 x 10'
NA
NA
9 x 10'
8 x 10"
5 x 10 4
Wl
5 x 10'
1 x 10s
1 X If)'1
3 x I01
3 x 1()4
NA
NA
NA
NA
4 x I01
W2
2 x 10'
5 x 10 7
3 x 10"
1 x 10'
1 x I04
2 x 10"
4 x 10"
NA
NA
2 x 10'

\V3
9 x 10"
2 x 10 7
2 x 10"
5 x 10"
6 x 10'
2 x 10"
4 x 10*
NA
NA
8 x I01
Volume V
Appendix V 16
12
-------
TABLE 13
Average Noncancer Hazard Indices for an Adult Subsistence Fanner
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Egg
Ingestion
Dairy
Ingestion
Vegetable
& Fmit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
HI
Subnrea
El
1 x 10'
2 x 10*
2 x 101
2 x I01
7 x 10"
3 x 10 !n
2 x 10"
NA
•*,
NA
4 x 10 '
E2
4 x 10*
9 x I07
7 x 10"
6 x 10"
4 x 10"
1 x 10'°
5 x 10'
NA
NA
2 x I01
E3
2 x 10*
4 x I07
3 x 10"
2 x I04
2 x 10"
4 x 10"
2 x 10"
NA
NA
7 x 10"
Nl
6 x 10*
! x 10*
1 x 101
8 x 10"
4 x 10"
NA
NA
NA
NA
2 x 10 '
N2
2 x 10*
4 x I07
3 x 10"
3 x 10"
1 x 10"
1 x 10'
3 x 10"
NA
NA
7 x 10"
N3
9 x I07
2 x 107
2 x 10"
1 x 10"
6 x 10'
NA
NA
NA
NA
3 x 10"
SI
5 x 10"
1 x 10*
8 x 10"
6 x 10"
4 x 10"
4 x 10'°
2 x 10"
NA
NA
2 x 10 '
S2
2 x 10*
4 x 107
3 x 10"
2 x 104
2 x 10"
NA
NA
NA
NA
6 x 10"
S3
7 x 10 7
2 x 107
1 x 10"
1 x 10"
7 x 10'
NA
NA
2 x 10"
4 x 10*
1 x 10"
\V1
6 x 10"
1 x 10*
1 x 10 1
9 x 10"
5 x 10"
NA
NA
NA
NA
3 x 10 '
VV2
3 x 106
6 x 10 7
4 x I04
3 x 10"
2 x 10"
5 x 10 '"
2 x 10"
NA
NA
1 x 10'

VV3
1 x 10"
3 x 10 7
2 x 10"
2 x 10"
1 x 10"
5 x 10 ln
2 x 10"
NA
NA
S x 101
Volume V
Appendix V-16
13
-------
TABLE 14
Average Noncanrer Hazard Indices for a Subsistence Fanner Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
f'-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Ijike
Ingestion
Lake
Dermal
Contact
Total
III
Subarea
El
8 x 10'
2 x 10"
4 x I01
1 x I0?
2 x 10'
2 x 10'
3 x 10s
NA
NA
2 x 10:
E2
3 x 10'
7 x I07
1 x 10'
5 x 10'
1 x 10'
6 x 10 '"
1 x 10s
NA
NA
7 x 10'
E3
1 x 10s
3 x 10'
6 x 10"
2 x 10'
5 x W
2 \ 10 ln
3 x 10'
NA
NA
3 x 101
Nl
4 x 10'
1 x 10*
2 x 10'
7 x 10'
1 x 10'
NA
NA
NA
NA
1 x 10-
N2
1 x 10'
3 x 10 7
7 x 10"
2 x 10'
5 x 10"
5 x 10"
5 x 10"
NA
NA
3 x 10'
N3
7 x 10*
2 x 107
3 x 104
1 x 10'
2 x 10"
NA
NA
NA
NA
2 x H)1
SI
3 x 10'
8 x 10 7
2 x 10'
5 x 10'
1 x 10'
2 x 10"
3 x 10s
NA
NA
8 x 10'
S2
1 x 10'
3 x I07
5 x 10 4
2 x 10'
5 x 10"
NA
NA
NA
NA
3 x 10'
S3
5 x 10*
1 x 107
2 x 10"
8 x 10 4
2 x 10"
NA
NA
9 x 10"
8 x 10"
1 x 10'
Wl
5 x 10'
1 x I06
2 x 10'
8 x 10'
2 x 10'
NA
NA
NA
NA
i x i
-------
TABLE 15
Maximum Cancer Risks for an Adult Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Kgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Subarea
El
3 x 10'°
1 x 10'°
1 x 107
2 x K)7
2 x 10"
4 x 10"
1 x 10"
NA
NA
4 x I07
E2
8 x 10"
4 x 10"
5 x 10"
8 x 10*
6 x 10 '
1 x 10"
4 x 10"
NA
NA
1 x 107
E3
3 x 10"
1 x 10"
1 x 10"
2 x 10"
2 x 10'
2 x 10"
1 x 10"
NA
NA
4 x 10"
Nl
2 x 10 '"
9 x 10"
6 x 10"
1 x K)'
7 x 10'
NA
NA
NA
NA
2 x 10 7
N2
5 x 10"
2 x 10"
2 x 10"
4 x 10"
3 x 10'
7 x 10"
7 x I012
NA
NA
6 x 10"
N3
2 x 10"
7 x 10"
6 x 10"
1 x 10*
7 x 10 I0
NA
NA
NA
NA
2 x 10"
SI
2 x 10'°
1 x 10 ln
8 x 10*
1 x 107
1 x 10"
6 x 10"
2 x 10"
NA
NA
2 x 10'
S2
4 x 10 "
2 x 10"
2 x 10s
4 x 10"
3 x 10"
NA
NA
NA
NA
6 x 10"
S3
1 x 10"
5 x I012
7 x 10"
1 x 10*
8 x 10 I0
NA
NA
6 x 10"
3 x 10"
2 x 10*
Wl
2 x 10'°
8 x 10"
9 x 10"
2 x I07
1 x 10"
NA
NA
NA
NA
1 x 10 7
\V2
5 x 10"
3 x 10"
3 x 10"
6 x 10"
4 x 10"
6 x 10"
2x 10"
NA
NA
9 x 10"
W3
1 x 10"
7 x 10"
1 x 10"
2 x 10*
1 x 10"
6 x 10"
2 x 10"
NA
NA
? x 10"
Volume V
Appendix V-16
15
-------
TABLE 16
Maximum Cancer Risks for a Child Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meal &
Kgg
Ingestion
Dairy
Ingestion
Vegetable
& E;niit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Stibarea
El
3 x 10"
2 x 10 to
1 x 10'
8 x 10'
2 x 10"
1 x 10"
2 x 10"
NA
NA
1 x 10*
E2
1 x 10'
6 x 10"
6 x 10*
3 x 10'
8 x 10"
3 x 10"
5 x 1012
NA
NA
3 x tO7
E3
3 x 10'°
2 x 10"
2 x 10*
8 x 10"
2 x 10'
8 x 10 "•
I x K)12
NA
NA
1 x 10'
Nl
2 x 10'
1 x 10 ">
7 x 10*
4 x I07
1 x 10"
NA
NA
NA
NA
4 x 107
N2
6 x 10 I0
4 x 10"
3 x 10"
1 x 107
4 x 10'
2 x 10 M
9 x 10"
NA
NA
2 x 10 '
N3
2 x 10 '"
1 x 10"
7 x 10'
4 x 10"
1 x 10"
NA
NA
NA
NA
4 x 10"
SI
3 x 109
2 x 10 '"
9 x 10*
5 x I07
1 x 10*
2 x 10"
3 x 10"
NA
NA
6 x K)7
S2
5 x 10 10
3 x 10"
2 x 10"
1 x 107
4 x 10'
NA
NA
NA
NA
2 x 10 7
S3
1 x 10'°
9 x 10 i:
7 x 10'
4 x 10*
1 x 10'
NA
NA
2 x 10"
4 x 10"
5 x 10"
Wl
2 x 10'
1 x 10 ln
1 x 10 7
5 x 10 7
2 x 10*
NA
NA
NA
NA
7 x 10 7
W2
7 x 10'°
4 x 10"
4 x 10*
2 x I07
5 x 10"
2 x 10"
3 x 10"
NA
NA
2 x 10'
W3
2 x 10 '"
1 x 10"
1 x 10"
6 x 10*
2 x K)'
2 x l()u
3 x 10"
NA
NA
1 x 10*
Volume V
Appendix V-16
-------
TABLE 17
Maximum Cancer Risks for a School-age Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
f^gg
Ingeslion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingeslion
Lake
Dermal
Contact
Total
Risk
Subarea
El
5 x 10 ln
1 x 10'°
2 x 10 7
5 x 10 7
2 x 10"
5 x 10"
1 x 10"
NA
NA
7 x 10'
E2
2 x 10'°
4 x 10"
5 x 10*
2 x 10'
6 x 10'
2 x 10"
4 x 10"
NA
NA
2 x 107
E3
5 x 10"
1 x 10"
2 x 10"
5 x 10"
2 x IOQ
4 x 10"
8 x 10"
NA
NA
7 x 10"
Nl
4 x 10 I0
1 x 10 ">
7 x 10*
2 x 10'
7 x 10'
NA
NA
NA
NA
3 x 10 '
N2
9 x 10"
3 x 10"
2 x 10"
8 x 10*
3 x 10'
1 x 10 M
6 x 10"
NA
NA
1 x 10 7
N3
3 x 10"
8 x 10"
7 x 10"
2 x 10"
7 x 10 I0
NA
NA
NA
NA
3 x 10"
SI
4 x 10'°
1 x 10'°
9 x 10"
3 x 107
1 x 10s
8 x 10"
2 x 10"
NA
NA
4 x 10 7
S2
7 x 10"
2 x 10"
2 x 10"
8 x 10"
3 x 10'
NA
NA
NA
NA
1 x 10'
S3
2 x 10"
6 x 10 "
1 x 10'
2 x 10"
8 x 10 10
NA
NA
8 x 10"
3 x 10"
1 x 10'
VVI
3 x 10 '"
8 x 10"
1 x I07
3 x I07
1 x 10"
NA
NA
NA
NA
4 x 10'
W2
9 x 10"
3 x 10"
4 x 10"
1 x I07
4 x 10'
9 x 10"
2 x 10"
NA
NA
2 x 10'
YV3
3 x 10"
7 x 10"
1 x 10"
4 x 10"
1 x 10'
9 x 10"
2 x 10"
NA
NA
5 x 10*
Volume V
Appendix V-16
17
-------

Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
f'-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
TABLK 18
Maximum Cancer Risks for an Adult Fanner
Subarea
El
2 x 10'
9 x 10 m
9 x 10'
7 x 10'
4 x 10'
8x10 '.'
3 x 10"
NA
*,
NA
2 x 10*
E2
5 x 10 10
3 x 10'°
3 x 10'
2 x 10'
1 x 10"
2 x 10"
9 x 1013
NA
NA
6 x 10'
E3
1 x 10'°
8 x 10"
9 x 10"
7 x 10s
4 x 10'
5 x 10"
2 x 10i:
NA
NA
2 x 10'
Nl
1 x 10"
6 x 10 '"
4 x 10'
1 x 10'
2 x 10"
NA
NA
NA
NA
7 x 10'
N2
3 x 10'°
2 x 10 I0
1 x 10'
1 x 10'
6 x 10'
1 x 10 u
2 x 10"
NA
NA
3 x 10'
N3
9 x 10"
5 x 10"
4 x IOR
3 x 10"
2 x 10"
NA
NA
NA
NA
7 x 10"
SI
1 x 10"
7 x 10'°
5 x 10 7
4 x 10 '
2 x 10"
1 x 10"
5 x 10"
NA
NA
1 x 10*
S2
2 x 10'°
1 x 10 10
1 x 10'
1 x 10 7
6 x 10"
NA
NA
NA
NA
3 x 10'
S3
6 x 10"
4 x 10"
4 x 10"
3 x 10"
2 x 10"
NA
NA
1 x 10 '"
7 x 10"
8 x 10"
Wl
9 x 10 '"
5 x 10 '°
6 x 107
4 x 10 7
3 x 10"
NA
NA
NA
NA
1 x 10"
\V2
3 x 10 10
2 x 10 I0
2 x 10 7
2 x 10 7
9 x 10"
1 x 10 '<
5 x 10"
NA
NA
4 x 10'
\V3
8 x 10"
5 x 10"
7 x 10*
5 x 10 "
3 x 10°
1 x 10 "
5 x 10"
NA
NA
1 x 10 7
Volume V
Appendix V-16
-------
TABLE 19
Maximum Cancer Risks for a Fanner Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
f"-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fniit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Suharea
El
3 x 10"
2 x 10 10
5 x 10 7
1 x 10*
2 x 10"
1 x 1()14
2 x 10"
NA
\
NA
2 x 10'
E2
1 x 10"
6 x 10"
2 x 10'
4 x 10'
8 x 10'
3 x 10"
5 x 10"
NA
NA
5 x 10'
E3
3 x 10ln
2 x 10"
5 x 10"
1 x l()7
2 x 10°
8 x 10"
1 x 10 |:
NA
NA
2 x I07
Nl
2 x 10"
1 x 10'°
2 x 10 7
5 x 10 7
1 x 10"
NA
NA
NA
NA
7 x 10 7
N2
6 x 10'"
4 x 10"
7 x 10*
2 x I07
4 x 10'
2 x 10 '"
9 x 10 "
NA
NA
2 x 10 7
N3
2 x 10 I0
1 x 10"
2 x IOR
4 x 10*
1 x 10'
NA
NA
NA
NA
7 x 10*
SI
3 x 10'
2 x 10'°
3 x 10 7
6 x 107
1 x 10*
2 x I014
3 x 10"
NA
NA
9 x 10 7
S2
5 x 10 I0
3 x 10"
7 x 10*
2 x 107
4 x 10*
NA
NA
NA
NA
2 x I07
S3
1 x 10'°
9 x IO'2
2 x 10"
5 x 10"
1 x 10'
NA
NA
2 x 10M
4 x 10"
7 x 10"
Wl
2 x 10'
1 x 10 ln
3 x K)7
7 x IO7
2 x 10"
NA
NA
NA
NA
1 x 10*
\V2
7 x 10 '"
4 x 10"
1 x IO7
2 x IO7
5 x 10'
2 x 10 M
3 x 10"
NA
NA
3 x 10'

W3
2 x 10 10
1 x 10"
3 x 10*
8 x 10"
2 x 10"
2 x 10 M
3 x 10"
NA
NA
1 x 10'
Volume V
Appendix V-16
19
-------
TABU-: 20
Maximum Cancer Risks for an Adull Subsistence Fanner
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Kgg
Ingest ion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Subarea
El
2 x ID'
9 x 10'°
2 x 10*
2 x 10"
2 x 10'
8 x 10"
3 x 10"
NA
NA
4 x 10"
E2
5 x 10 in
3 x 10'°
7 x I07
6 x 10'
5 x 10"
2 x 10"
9 x 10 l2
NA
NA
1 x 10"
FJ
1 x 10'°
8 x 10"
2 x 10 7
2 x 10 '
2 x 10"
5 x 10"
2 x 1012
NA
NA
4 x 10 7
Nl
1 x 10"
6 x 10 ln
9 x 10 7
7 x 10 7
7 x 10"
NA
NA
NA
NA
2 x l()6
N2
3 x 10'°
2 x 10 '"
3 x 10 7
3 x 10'
2 x 10"
1 x 10 M
2 x 10"
NA
NA
6 x 107
N3
9 x 10"
5 x 10"
9 x 10"
7 x 10"
7 x 10'
NA
NA
NA
NA
2 x 10 7
SI
1 x 10"
7 x 10'°
1 x 10*
1 x 10*
9 x 10"
1 x 10 M
5 x 10"
NA
NA
2 x 10"
S2
2 x 10'°
1 x 10'°
3 x 107
3 x I07
2 x 10"
NA
NA
NA
NA
6 x 10'
S3
6 x 10"
4 x 10"
1 x I07
8 x 10"
7 x I09
NA
NA
1 x 10 H
7 x 10 n
2 x 10'
VVI
9 x 10'"
5 x 10 I0
1 x 10"
1 x 10*
1 x I07
NA
NA
NA
NA
3 x 10"
W2
3 x 10 '"
2 x 10 '"
5 x 107
4 x 10 7
4 x 10"
1 x 10 M
5 x 10"
NA
NA
9 x It)'
W3
8 x 10"
5 x 10"
2 x l()7
1 x 10 7
1 x 10"
1 x 10 M
5 x 10"
NA
NA
3 x 10'
Volume V
Appendix V 16
20
-------
TABU: 21
Maximum Cancer Risks for a Subsistence Fanner Child
Exposure
Pathway
Soil
Ingeslion
Soil
Dermal
Contact
Meat &
Kgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Risk
Subarea
El
3 x 10"
2 x 10 I0
1 x 10*
1 x 10*
1 x 10 7
1 x 10 "
2 x 10"
NA
>>
NA
4 x 10*
E2
1 x 10"
6 x 10"
4 x It)7
9 x 10'
.1 x 10"
3 x 10"
5 x 10"
NA
NA
1 x 10*
E3
3 x 10'°
2 x 10"
1 x 10'
1 x 10'
1 x 10"
8 x 10'"
1 x I012
NA
NA
4 x 107
Nl
2 x IO9
1 x 10'"
5 x 10 7
1 x 10*
4 x 10"
NA
NA
NA
NA
2 x 10"
N2
6 x 10'°
4 x 10"
2 x 10 7
4 x It)7
2 x 10"
2 x 10 l4
9 x 1012
NA
NA
6 x 10 7
N3
2 x 10 '"
1 x 10"
5 x 10"
1 x 10 7
4 x 10'
NA
NA
NA
NA
2 x 10 7
SI
3 x 109
2 x 10'°
6 x It)7
2 x 10*
6 x 10s
2 x It)14
3 x 10"
NA
NA
2 x 10*
S2
5 x It)10
3 x 10"
2 x 10 '
4 x 107
2 x 10"
NA
NA
NA
NA
6 x 10 7
S3
1 x 10'°
9 x 10"
5 x 10s
1 x I07
5 x 10"
NA
NA
2 x IO'4
4 x 10 '2
2 x 10 7
Wl
2 x 10'
1 x 10 10
7 x IO7
2 x 10*
6 x 10"
NA
NA
NA
NA
2 x 10*
W2
7 x 10 '"
4 x 10"
2 x IO7
6 x IO7
2 x 10"
2 x 10 '4
3 x 10"
NA
NA
9 x 10'
W3
2 x 10"'
1 x 10"
8 x 10"
2 x IO7
7 x 10"
2 x 10 u
3 x 10"
NA
NA
} x IO7
Volume V
Appendix V-16
21
-------
TABLE 22
Maximum Noiicancer Hazard Indices for an Adult Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Egg
Ingeslion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
Hi
Sufoarea
El
1 x 10'
2 x 10*
6 x I04
1 x 10'
5 x I')4
8 x I0in
3 x 10"
NA
NA
2 x 10'
E2
3 x 10*
6 x I07
2 x 10"
4 x 10"
2 x 10"
2 x 10 10
9 x 109
NA
NA
7 x 10"
E3
1 x 10*
2 x 10'
6 x 10'
1 x 10"
5 x 10'
6 x 10"
2 x 10"
NA
NA
2 x 10"
Nl
7 x 10*
1 x 10*
5 x 10"
7 x 10"
2 x 10"
NA
NA
NA
NA
1 x If)1
N2
2 x 10*
3 x H)7
1 x 10 4
2 x 10"
7 x 10'
2 x If)9
7 x 10"
NA
NA
4 x 10"
N3
6 x U)7
i x 107
4 x 10'
6 x 10'
2 x 10'
NA
NA
NA
NA
1 x 10 1
SI
8 x 10*
I x 10*
5 x 10"
8 x 10^
3 x I04
1 x 10'
4 x 10s
NA
NA
2 x 10 1
S2
I x 10*
3 x 107
9 x 10'
2 x 10"
7 x 10'
NA
NA
NA
NA
3 x 10'
S3
4 x I07
9 x 10*
3 x 10'
5 x 10'
2 x 10'
NA
NA
3 x 10"
7 x 10"
1 x 10'
Wl
5 x 10*
1 x 10*
3 x 104
7 x I04
3 x 104
NA
NA
NA
NA
1 x 10'
W2
2 x 10*
4 x 10 7
1 x 10 4
2 x I04
1 x 10"
1 x If)9
5 x 10"
NA
NA
4 x I01
W3
6 x If)7
1 x If)7
3 x 10'
6 x If)'
3 x 10'
1 x W
5 x 10"
NA
NA
1 x 10"
Volume V
Appendix V-16
22
-------
TABLE 23
Maximum Noncancer Hazard Indices Tor a Child Resident
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Egg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
III
Subarea
El
2 x 10"
5 x 10'
1 x 10'
1 x 10 7
1 x 10'
4 x 10'
5 x 10s
NA
NA
1 x 10 :
E2
6 x 10s
1 x 10*
4 x 10"
3 x I01
4 x 10"
1 x 10'
2 x 10"
NA
NA
4 x K)1
E3
2 x 10<
5 x I07
1 x 10"
9 x 10"
1 x I04
3 x 10 I0
4 x 10"
NA
NA
1 x K)1
Nl
1 x 10"
3 x 10s
9 x 10"
6 x 10'
5 x 10"
NA
NA
NA
NA
8 x 10'
N2
3 x 10s
8 x 107
2 x K)4
2 x I01
2 x 10"
1 x 10*
1 x 107
NA
NA
2 x K)1
N3
1 x K)'
2 x K)7
7 x 10'
5 x 10"
5 x 10s
NA
NA
NA
NA
7 x 10 4
SI
2 x 10"
3 x 10*
1 x K)1
7 x 101
7 x 10"
5 x 10"
8 x 10"
NA
NA
9 x K)1
S2
3 x 10s
7 x 107
2 x K)4
1 x H)1
2 x 10^
NA
NA
NA
NA
2 x 10'
S3
8 x I06
2 x 10 7
5 x 10'
4 x 10"
6 x 10s
NA
NA
1 x 10"
1 x 10 7
•5 x K)4
Wl
9 x 10'
2 x I06
6 x 10"
6 x 101
8 x \tf
NA
NA
NA
NA
7 x 10'
W2
4 x 10s
9 x 10 7
2 x 10"
2 x 10'
3 x 10"
6 x 10"
9 x 10"
NA
NA
2 x 10'
VV3
1 x 10s
3 x in7
6 x 10'
5 x 10"
9 x 10 5
6 x 10"
9 x 10"
NA
NA
7 x 10*
Volume V
Appendix V-16
-------
TABLE 24
Maximum Noncancer Hazard Indices for a School-age Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Egg
Ingestion
Dairy
Ingeslion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
ill
Suharea
El
3 x 10'
3 x 10s
1 x 10'
5 x 10'
8 x H)4
2 x 10°
4 \ 10"
NA
NA
7 x 101
El
9 x 10*
1 x 10*
3 x HT1
2 x I01
3 x 10"
5 x 10 '"
1 x 10*
NA
NA
2 x 101
E3
3 x 10*
3 x 10'
1 x 10"
5 x 10 4
8 x 10'
1 x 10"'
3 x 10"
NA
NA
7 x 10"
Nl
2 x 10'
2 x 10*
8 x 10"
3 x H)1
1 x H)4
NA
NA
NA
NA
4 x 10'
N2
5 x 10*
5 x 107
2 x H)4
9 x 10"
1 x 10"
5 x 10'
9 x 10"
NA
NA
1 x 10'
N3
2 x 10*
2 x I07
6 x 105
3 x 104
3 x 10'
NA
NA
NA
NA
4 x l()4
SI
2 x 10s
2 x 10*
9 x 10"
4 x 101
5 x 10"
3 x 10'
6 x 10"
NA
NA
5 x 10'
S2
4 x 10*
4 x 107
1 x 10"
7 x 10"
1 x 10"
NA
NA
NA
NA
1 x 101
S3
1 x 10*
1 x 10 7
4 x 10'
2 x 10"
4 x 10'
NA
NA
6 x 10'
9 x 10"
3 x It)'1
Wl
1 x 10'
2 x 10*
5 x 10"
3 x 10 1
5 x 10"
NA
NA
NA
NA
4 x H)'
W2
5 x 10*
6 x I07
2 x 10"
I x 10'
2 x 10"
3 x !()'
6 x 10"
NA
NA
I x 10'
VV3
2 x 10*
2 x 10'
5 x 10'
3 x 10 4
6 x 10'
3 x 10°
7 x 10"
NA
NA
4 x 10'
Volume V
Appendix V-16
24
-------
TAKLE 25
Maximum Noncancer Hazard Indices for an Adult Fanner
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
F-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fniit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
HI
Suharea
El
2 x 10'
6 x 10*
2 x I01
1 x H)1
5 x l()4
8 x H)'"
3 x 10"
NA
NA
4 x 101
E2
8 x 10"
2 x 10*
6 x \0^
4 x 10"
2 x 10"
2 x 10'°
9 x 10"
NA
NA
1 x 101
E3
2 x 10"
6 x 107
2 x 10"
1 x 10"
5 x 10s
6 x 10"
2 x 10'
NA
NA
4 x 10"
Nl
2 x 10s
4 x 106
1 x I01
9 x 10"
2 x 10"
NA
NA
NA
NA
3 x I01
N2
4 x 10*
1 x 10"
4 x 10"
3 x 10"
7 x 10s
2 x 10"
7 x 10"
NA
NA
7 x 10"
N3
1 x 10*
3 x H)7
1 x 10"
8 x 10'
2 x 10'
NA
NA
NA
NA
2 x 10"
SI
2 x 10'
4 x 10*
2 x 101
1 x 101
3 x 10"
1 x 109
4 x 10*
NA
NA
3 x 10 '
S2
4 x 10'
8 x I07
3 x 10"
2 x 10"
7 x 10'
NA
NA
NA
NA
5 x 10"
S3
1 x 10*
3 x 10 7
8 x I01
6 x 10'
2 x 10'
NA
NA
3 x 10"
7 x 10"
2 x 10"
\V1
1 x 10'
3 x 10s
1 x I01
8 x 10"
3 x \Q*
NA
NA
NA
NA
2 x 10 '

W2
5 x 10*
1 x 106
4 x 10"
3 x 10"
1 x 10"
1 x 10"
5 x 10"
NA
NA
7 x K)1

VV3
1 x 10'
3 x 10 7
1 x 10"
8 x 10'
3 x 10'
1 x 10'
5 x 10s
NA
NA
2 x 10"
Volume V
Appendix V-16
-------
TABLE 26
Maximum Noncancer Hazard Indices for a Fanner Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
Kgg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Uke
Ingestion
Uke
Dermal
Contact
Total
111
Suharea
El
2 x 10"
5 x 10<
4 x 10'
1 x 10 :
1 x 10'
4 x 10"
5 x 10"
NA
NA
2 x 102
E2
6 x 10'
1 x 10*
1 x I03
4 x 10'
4 x 10"
1 x 10'
2 x 10*
NA
NA
5 x 101
E3
2 x 10'
5 x H)7
3 x H)4
1 x 10'
1 x 10"
3 x 10'"
4 x 10"
NA
NA
2 x I01
Nl
1 x 10"
3 x 10*
3 x 10 '
8 x 10'
5 x 10"
NA
NA
NA
NA
1 x 10*
N2
3 x 10'
8 x 107
7 x 10"
2 x 10'
2 x 10"
1 x 10"
1 x 10'
NA
NA
3 x 10 '
N3
1 x 10s
2 x 107
2 x 10"
6 x 10"
5 x 10'
NA
NA
NA
NA
9 x 10"
SI
2 x 10"
3 x 106
3 x I01
9 x H)1
7 x 10"
5 x 10'
8 x 10"
NA
NA
1 x W-
S2
3 x 10'
7 x I07
5 x 10"
2 x 101
2 x 10"
NA
NA
NA
NA
2 x 10'
S3
8 x 10*
2 x 107
2 x 10"
5 x 10"
6 x 10'
NA
NA
1 x 10"
1 x 10 7
7 x 10 '
Wl
9 x 10'
2 x 10*
2 x 10 1
7 x H)1
8 x 10"
NA
NA
NA
NA
I x 10'
W2
4 x 10'
9 x I07
7 x 10"
2 x 10'
3 x 10"
6 x 10"
9 x 10"
NA
NA
1 x 10'
W3
1 x 10'
3 x 10 7
2 x 104
7 x 10"
9 x 10'
6 x 10"
9 x 10"
NA
NA
9 x 10"
Volume V
Appendix V-)f>
26
-------
TABLE 27
Maximum Nuncancer Hazard Indices lor an Adult Subsistence Fanner
Hxposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
F-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fruit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
111
Sub area
El
2 x 10s
6 x 10*
4 x 103
4 x K)1
2 x 10'
8 x 10 l(1
3 x 10*
NA
NA
1 x 10:
E2
8 x 10*
2 x 10*
1 x 10'
1 x 10'
8 x It)4
2 x 10 I0
9 x 10"
NA
NA
3 x I01
FJ
2 x 10*
6 x I07
4 x K)4
3 x 104
2 x l()4
6 x 10"
2 x 10"
NA
NA
1 x I01
Nl
2 x 10'
4 x 10*
3 x 10'
2 x 10'
1 x 10'
NA
NA
NA
NA
6 x 10'
N2
4 x 10*
1 x 10*
8 x 104
6 x 10"
4 x K)4
2 x 10'
7 x 10"
NA
NA
2 x 10'
N3
1 x 10*
3 x 107
3 x I04
2 x 10 4
1 x 10"
NA
NA
NA
NA
5 x 10"
SI
2 x 10s
4 x 10*
4 x K)3
3 x 10 3
1 x 10'
1 x 10'
4 x 10"
NA
NA
8 x K)'
S2
4 x 10*
8 x 107
6 x 10^
5 x 10"
3 x \04
NA
NA
NA
NA
1 x 10'
S3
1 x 10*
3 x I07
2 x 10"
1 x 10 4
1 x U)4
NA
NA
3 x 109
7 x 10"
4 x I04
\VI
1 x 10'
3 x 10*
2 x 10'
1 x 10'
1 x I01
NA
NA
NA
NA
6 x K)'
W2
5 x 10"
I x 10s
8 x 10"
7 x I04
5 x I04
1 x 10'
5 x 10*
NA
NA
2 x K)1
\V3
1 x 10*
3 x K)7
2 x I04
2 x If)4
2 x 10 4
1 x 10'
5 x 10"
NA
NA
fi x I04
Volume V
Appendix V  16
27
-------
TABI.K 28
Maximum Noncancer Hazard Indices for a Subsistence Fanner Child
Exposure
Pathway
Soil
Ingestion
Soil
Dermal
Contact
Meat &
F-gg
Ingestion
Dairy
Ingestion
Vegetable
& Fmit
Ingestion
River
Ingestion
River
Dermal
Contact
Lake
Ingestion
Lake
Dermal
Contact
Total
HI
Subarea
El
2 x 104
5 x 10 6
8 x I01
3 x 1():
8 x 10'
4 x 10'
5 x 10s
NA
V
NA
5 x 10 2
E2
6 x 10'
1 x 10*
3 x 101
9 x 10'
3 x 10'
1 x 10'
2 x I08
NA
NA
1 x I02
E3
2 x 10'
5 x I07
8 x 10 4
3 r 10'
8 x IO"
3 x 10'"
4 x 10'
NA
NA
4 x 10'
Nl
1 x 10"
3 x 10*
6 x 10'
2 x 10 2
3 x 10'
NA
NA
NA
NA
3 x l()2
N2
3 x 10'
8 x 10 '
2 x 10'
5 x 10'
1 x 10'
1 x 10s
1 x 10 7
NA
NA
8 x 10'
N3
1 x 10'
2 x 101
5 x 10"
2 x K)1
3 x 10"
NA
NA
NA
NA
2 x K)1
SI
2 x 10"
3 x 106
7 x 10'
2 x 10 2
4 x I01
5 x 109
8 x 10s
NA
NA
3 x I02
S2
3 x 10'
7 x I07
1 x 10'
4 x 10'
1 x I03
NA
NA
NA
NA
6 x 10'
S3
8 x 10*
2 x 107
4 x 10"
1 x H)1
4 x 10"
NA
NA
1 x 10*
1 x K)7
2 x 10'
Wl
9 x 10'
2 x 10*
4 x 10'
2 x 102
5 x 101
NA
NA
NA
NA
3 x 10'
VV2
4 x 10'
9 x K)7
2 x 10'
6 x 10 '
2 x I01
6 x 10"
9 x K)"
NA
NA
9 x K)'
W3
I x 10'
3 x 101
4 x 10"
2 x I01
6 x 10"
6 x 10"
9 x 10"
NA
NA
3 x 10'
Volume V
Appendix V-16
28
-------
                            APPENDIX V-17

            Estimation of High-end Cancer Risks and Hazard Quotients
                 for Subsistence Farmer and Child in Subarea El
Volume V
-------
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ABLE 1  Avg A Hiqli rnd r.m.
                                   LIFETIME AVERAGE DAILY DOSE (LADD) FOR CHEMICALS WITH CARCINOGENIC HEALTH EFFECTS
Chemical
3.7.8 TCDD
2 3.7.8 PeCDD
2.3.4.7.8 HirCDD
2.3.8.7.8 HxCDD
2.3.7.8.9 HxCDD
2.3,4,6,7.8-HpCDD
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3.7,8-TCDF
2.3.7.8 PeCDF
3,4.7,8PeCDF
2.3.4.7.8-HxCDF
2,3.6 7.8-HxCDF
2.3.7.8.9-HxCDF
3.4.8.7,8 HxCDF
I 2,348 78-HpCDF

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CDF
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ruo(a)pyrene
j inzo(b)fluonanlhene
I s(2-»thylne»yl)phlhalale
j inbon letrachloride
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j (n)ocfyl phlhalale
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t ixachlorobenzane
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xachlorophdna
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E t hi end
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mgAYg d
t IE 17
55E-17
3E-17
5E 17
5E-17
9E-17
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2E-18
28E-16
27E-18
39E-18
3 7E-18
85E-17
4 2E-16
1 IE-IS

1 5E-16
66E-16
32E-14
94E 15
46E-1S
53E 13
20E 12
39E 14
1 5E^»
58E-13
4 IE-IS
8 7E-18
86E-12
39E-11
25E-13
54E-13
70E-13
1 1E-11
35E-11
2 3E-10
90E-1S
3SE-11
59E-13
72E-11
3 7E-08
44E-11
20E-09
1 3E-10
26E 12
84E-09
Leafy
Pioduce
Ingestion
mg/kg-d
54E 15
9 BE t4
1 4E 13
3 7£ 14
42E 14
22E 12
28E-10
806-14
49E-13
66E-13
45E-13
1 OE-12
23E-13
74E-13
2 4E-12

1 9E-13
6 1E-11
7 1E-13
1 3E-12
4 1E-11
46E-09
22E 09
25E 06
39E-10
99E-12
4 BE 07
2 1E-12
1 2E-11
12E-11
20E-13
57E-11
1 OE 11
23E 11
98E-11
74E-10
49E-14
49E-11
98E-13
1 4E-10
5 5E-08
16E-11
99E 10
1 SE-10
35E-11
3 7E-09
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Inqoslion
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24E 17
1 2E 16
70E 17
1 7E 16
1 1E-16
73E-16
49E-15
22E-18
63E-16
73E-16
1 5E 15
1 4E-15
33E 16
1 6E-15
6 7E 15

8 7E-16
80E 15
56E 13
8 7E-14
5 2E 13
1 5E 13
53E 12
1 4E 13
43E 10
2 4E-12
1 OE-10
5 1E 14
49E 10
1 5E-10
70E 12
S6E 10
26E-12
25E 14
25E-14
41E-13
1 5E-18
1 2E 13
75E-17
95E-14
1 4E 11
2 16-15
5 7E-13
30E 13
1 8E 16
2 5E 12
E«poii>d
Fiuit
Inqeslinn
mq'kq d
2 3E-16
40E 15
55E-I5
1 9E 15
1 9E-15
89E 14
t IE-It
33E-15
20E-I4
27E-14
2 1E-14
43E-14
97E-15
3 3E-14
1 2E-13

1 OE-14
24E-12
6 1E-14
59E-14
1 6E 12
1 9E-10
88E-11
9 7E 08
1 5E-09
1 5E-11
1 9E-08
83E-14
90E-12
39E 11
25E-13
85E-11
15E-11
1 7E-11
90E-11
45E-10
59E-14
59E 11
1 7E-12
1 4E-10
3 7E-08
5 1E-11
2 7E 09
1 5E 10
54E 11
8 5E 09
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mq'hq d
2 7E 17
1 3E 16
3 2E 17
1 IE 16
36E 17
24E 16
26E 15
28E 16
64E-18
66E 16
96E-16
89E-16
2 1E-16
1 OE 15
7 ME ic
L OL 13
35E-16
16E 15
7 7E-14
23E-14
1 1E-14
1 3E-I2
4 BE 12
94E-14
37E-09
14E-12
99E-15
2 IE 15
2 IE-It
94E-11
61E-13
13E-12
1 7E-12
26E-11
84E-11
55E-10
22E-14
84E-11
14E-12
1 7E-10
8 9E-08
1 1E-10
4 6E-09
31E 10
62E 12
2QE 08
Rivot
Walei
Inqnslinn
niq'Vq d
66E 22
32E.21
84E 22
33E 21
2 IE 21
48E-21
7 5E-20
63E-21
1 7E-20
1 9E 20
30E 20
2 8E-20
64E-21
3 IE 20
fi flF 7(1
D OC"*U
8 7E-21
1 9E 20
1 4E-18
1 1E-18
1 3E-18
22E-17
82E-17
4 1E-17
40E-16
50E-17
22E-18
4 2E-20
2 3E-18
26E-18
3 7E-18
22E-16
56E-17
87E-17
19E 15
39E-15
22E 18
84E-17
49E 17
30E-15
4 1E-14
2 3E 16
2 7E-14
3 IE 16
2 4E 15
2 3E 15
Rivpr
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Dormat
Corilarl
niqfVq d
2 8E 18
1 1E-17
1 5E-17
26E-17
3 7E-17
1 3E 16
58E-16
25E-17
83E-17
1 IE 18
26E-16
24E-16
56E-17
2 7E-16
1 "Jf 1C
1 iC-13
1 6E-18
1 2E-15
36E-15
88E-1S
1 9E-14
64E-14
28E-13
32E-13
94E-15
32E-13
S9E-14
6BE-17
3 7E-13
8BE-14
30E-15
23E-12
34E-13
32E-17
69E-18
1 4E-15
80E-19
30E-17
18E-17
1 1E-15
1 5E 14
83E-17
99E-15
1 1E-16
89E 16
82E 16
Lake
Walnr
Ingnstion
mq/kq d
NA
NA
NA
• NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lakn
Wain
Dermal
Contact
n«|/kq d
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Infant
Binasl milk
Inqnstinn
mi) (kg d
25E-13
4 1E-12
2 8E-12
7 8E-13
1 1E-12
94E-12
1 6E-09
82E-13
3 9E-12
2 1E-11
1 2E-11
22E-11
4 9E-12
1 4E-11

1 3E-1 1
24E-12
1 6E-10
62E-11
40E-11
96E-10
4 7E-07
3 4E-07
70E-06
1 1E-11
2 6E-07
3 8E-03
42E-10
2 7E-09
92E-11
1 2E-11
7 2E-05
2 2E-07
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ume V. Appendu V 17
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                                         CARCINOGENIC RISKS
Chemical
'.3.7.8-TCDD
1. 2,3. 7.8 PeC DO
f.2.3.4.7.8-HxCDO
I.2.3,8.7.8-HKCDD
I 2.3 7 8,9-HxCDD
1.2.3,4.8,7.8 HpCDO
3CDD
J.3.7.8TCDF
1. 2.3.7,8 PeCDF
!.3.4.7.8-PoCDF
1 2.3 4.7 8-HxCDF
1,2.3.6.7,8-HxCDF
1 2.3 78.9-HxCDF
!.3.4 8.7,8 H«CDF
1 2,3 4 6.7 8-HpCDF
1.2.3,4. 7.8 9-HpCDF
3CDF
r elrachloroblphenyt
toKachlorob'phenyl
teplachlorobiphenyl
)en;o(a)pyrane
!enzo(b)ft'K>canlh<"i«
Ii5( '-elhythexyljpliltialaln
Carbon lalrachlortde
)lbenz(«,h)anthtac«ne
3l(n)octyi phlhalale
taplac.ilor
te»achloiob«nzene
foxachloiobutadiene
1exachlorocyclop«ntadiene
lexachlofophene
ndeno(1,2,3-cd)pvrane
Kntlmony
Vreenic
larlum '
isrytlium
ladmium
Chromium (he«avalent)
ead
Mercury
Jicknl
ielnnium
iflver
halluim
'me
DIOXIN TEQ
ORGANICS TOTAL (non dioxm)
INORGANICS TOTAL
SUBAREA TOTAL
Suhaiea
El avg
E1 avg
El avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avfl
El avg
El avg
El avg
El avg
E1 avg
El avg
E1 avg
El avg
El avg
E1 avg
El avg
E1 avg
El avg
E1 avg
E1 avg
Ef avg
El avg
El avg
E1 avg
El avg
E1 avg
E1 avg
El avg
El avg
E1 avg
El avg
El avg
El avg
El avg
Soil
Inqpilion
Risk
96E 12
24E 11
5 3E 12
94E 12
60E 12
89E 12
34E-12
86E 12
1 4E 11
1 7E-10
83E-11
78E 11
1 8E 11
8 BE 11
5 3E 11
68E 12
1 OE 11
5 2E 13
BSE 13
8 3E 13
1 2E 11
4 BE 12
79E 15
49E 13
2 7E-11
NT
1 4E-14
98E-12
1 3E-12
NT
NT
31E-12
NT
4 7E-11
NT
3 1E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
60E-10
6 IE 11
48E 11
70E-10
Soil
Dpimal
Conlart
Risk
52E-12
1 3E 11
29E 12
5 1E-12
33E-12
3 BE 12
1 8E-12
47E-12
76E-12
93E-11
45E-11
42E-11
9 BE 12
4 BE 11
29E 11
3 7E 12
56E 12
28E 13
46E 13
45E 13
1 3E 1 1
52E 12
8 7E 15
54E 13
30E 11
NT
1 8E-14
1 1E-11
1 4E-12
NT
NT
34E-12
NT
86E-12
NT
56E-M
NT
NT
NT
NT
NT
NT
NT
NT
NT
32E-10
6SE 11
B6E 12
40E-10
Bnel
iMqeslinn
Risk
6 1E 09
52E 08
70E 09
1 9E 09
26E 09
20E 09
3 7E 08
1 9E 09
45E09
26E 07
29E 08
5 3E 08
1 2E 08
35E 08
2 8E 09
5 7E 10
3 IE 09
89E 11
4 4E 11
1 2E 09
96E 08
5 7E 09
1 5E 08
72E-14
1 4E-OS
NT
3 BE It
98E-11
86E-13
NT
NT
1 3E-09
NT
25E-10
NT
33E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 1E-07
1 3E-07
25E 10
6 4E 07
Poik
loqrslinn
Riik
66E 10
4 2E 09
55E 10
2 IE 10
25E 10
1 6E-10
26E 09
1 BE -10
37E-10
2 IE 08
30E 09
45E 09
1 OE 09
33E 09
30E 10
73E 11
2 3E 10
2 2E-11
1 4E 11
9 7E 11
26E 09
1 9E 10
4 1E 10
12E 14
6BE-10
NT
1 2E-12
37E-11
4 1E-U
NT
NT
70E-11
NT
35E-11
NT
1 2E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 3E 08
42E 09
35E 11
4 7E 08
Chickfn
Inqpstiim
Risk
3 5E 11
BSE 11
9 IE t?
1 4E 11
1 1E It
2 1E 12
1 5E 12
70E 12
8 7E 12
45E 10
1 6E 10
1 3E 10
30E 11
1 3E 10
1 8E 11
5 7E 12
1 7E 12
2 7E 12
1 6E 12
1 6E 12
1 8E 13
90E 14
19E 17
74E 17
1 6E-12
NT
3 1E 16
96E 14
1 1E-15
NT
NT
1 6E-13
NT
1 9E-11
NT
63E-15
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E 09
80E 12
1 9E 11
1 IF 09
Olhpl
Poultry
Inqpslion
Risk
96E 12
2 3E 11
25E 12
3 BE 12
3 1E 12
5 7E 13
40E 13
1 9E 12
2 3E 12
1 2E 10
45E-11
36E 11
82E 12
36E 11
50E 12
1 6E 12
4 7E 13
7 IE 13
43E 13
44E 13
4 BE 14
24E 14
50E 18
20E-17
4 3E-13
NT
84E 17
26E-14
30E-16
NT
NT
44E-14
NT
51E-12
NT
1 7E-15
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E 10
2 2E 12
5 IE 12
3 IE 10
Egg
liiqnsluin
Risk
2 2E 11
5 3E 11
5 7E 12
BSE 12
72E 12
1 3E 12
93E 13
44E 12
55E 12
29E 10
1 OE 10
83E 11
1 9E 11
B4E 11
1 2E-11
36E 12
1 IE 12
1 7E-12
1 OE 12
IDE 12
10E 10
52E 11
1 1E-14
42E-14
91E-10
NT
1 BE 13
55E-11
84E-13
NT
NT
94E-11
NT
1 1E-11
NT
34E-15
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E 10
1 2E 09
1 1E 1t
1 9E 09
TOTAL
MEAT f.
EGG
INGEST ION
RISK
69E 09
56E 08
76E 09
2 1E 09
2 BE 09
22E 09
39E 08
2 IE 09
49E 09
28E 07
32E 08
5 BE 08
1 3E 08
3 9E 08
3 IE 09
65E-10
3 3E 09
96E 11
61E-11
1 3E-09
9 9E-08
59E-09
1 6E 08
13E-13
1 6E-08
NT
39E-11
1 9E 10
1 9E-12
NT
NT
15E-09
NT
32E-10
NT
4 5E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
55E 07
1 4E 07
32E 10
69E 07
Milk
liiqrr.lnni
Risk
1 IE 09
89E 09
t 2E 09
32E 10
44E 10
35E 10
63E 09
33E-10
7 7E 10
4 4E-08
5 OE 09
9 1E 09
2 IE 09
6 OE 09
48E-10
98E 11
53E 10
12E 11
76E-12
2 IE 10
8 6E-08
5 1E-09
1 4E 08
7 1E-14
1 3E-08
NT
34E-11
89E-11
79E-13
NT
NT
1 2E-09
NT
2 1E-11
NT
84E-16
NT
NT
NT
NT
NT
NT
NT
NT
NT
8 7E 08
1 ?E O/
2 IE 11
7 IF 07
Choose
Inqnslion
Risk
1 4E 09
1 2E 08
1 6E 09
42E 10
5 BE 10
45E 10
8 2E 09
43E-10
10E 09
5 8E 08
65E 09
1 2E-08
2 7E 09
79E09
63E-10
1 3E-10
69E 10
1 5E 11
99E-12
2 7E-10
7 5E-09
44E 10
1 2E-09
62E-15
1 1E-09
NT
30E-12
78E-12
69E-14
NT
NT
10E-10
NT
1 8E-12
NT
73E-17
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 IE 07
1 IE 08
1 8E 12
1 ;r 07
Milk
Desseits
Inqeslion
Risk
74E 10
63E 09
BSE 10
23E 10
3 IE 10
25E 10
4 BE 09
23E 10
55E 10
3 IE 08
35E 09
64E09
15E09
43E09
34E 10
69E 11
3 7E 10
84E 12
53E 12
1 5E 10
94E09
55E 10
1 5E^)9
7 7E-15
1 4E-09
NT
37E-12
9 7E-12
86E-14
NT
NT
1 3E-10
NT
23E-12
NT
91E-17
NT
NT
NT
NT
NT
NT
NT
NT
NT
62E 08
t 3E 08
2 IE 12
7 r,r OB
Yogurt
Inqeslinn
Risk
34E 11
29E 10
39E 11
10E 11
t 4E-11
1 IE 11
21E-10
1 IE 11
25E 11
14E09
16E 10
30E 10
6BE-11
20E 10
16E 11
32E 12
1 7E 11
39E 13
25E-13
68E 12
28E09
16E 10
44E-10
23E-15
42E-10
NT
1 IE 12
29E 12
26E-14
NT
NT
39E-11
NT
89E-13
NT
27E-17
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 9E 09
3 9E 09
6 9t 13
6 7F OT
Ctpam
Ingoslinn
Risk
29E 10
2 4E 09
33E 10
B7E 11
1 2E-10
95E 11
1 7E 09
90E 11
2 IE 10
1 2E 08
1 4E 09
2 SE 09
56E 10
16E09
1 3E-10
2 7E 11
1 4E 10
32E 12
2 IE 12
57E 11
19E09
1 IE 10
30E 10
15E 15
28E-10
NT
74E 13
19E 12
1 7E 14
NT
NT
26E 11
NT
46E 13
NT
1 8E 17
Nt
NT
(Jl
NT
NT
NT
NT
m
Nt
? 4E OB
26f 09
461 13
7 fir OB
Buttot
Inqeslion
Risk
1 4E 09
1 2E 08
1 6E-09
43E 10
59E-10
4 7E 10
B4E 09
44E 10
1 OE 09
S 9E 08
« 7E 09
1 2E 08
2 BE 09
B1E 09
64E 10
1 3E 10
70E 10
16E 11
10E 11
2 BE 10
2 BE 09
16E 10
44E 10
23E 15
42E-10
NT
1 1E 12
29E 12
26E-J4
NT
NT
39E-11
NT
69E-13
NT
2 7E-17
NT
NT
NT
NT
NT
NT
nr
NT
NT
1 2E 07
42E 09
69E 11
1 7F 07
nlume V, Appondi* V-17
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                                   ^UI9  WfOJk-*NJMU>— -W-*d»O»K*-*tl*«»
-------
                     V    /
ARI E 1 Avq f. Hiqh rml C.in, ri Ri.,1.--, A Nnnc .1.1, €•( HO'.
                                                                        i  A.lull
                                          NONCARCINOGFNIC HA7ARD OUOTIFN1'

Chemical

>.3.7.8 TCOD
23 7 8 PeCDO
.2.3,4.7,8 HxCDD
.2.3.6.7.8 HxCDD
.2 3.7.8,9 HxCDD
.2.3,4.6.7,8 HpCDD
3CDD
,3.7.8-TCDF
,2.3.7.8-PeCDF
.3.4.7.8 PeCDF
.2.3.4. 7.8 HxCDF
2.38 7,8-HxCDF
.2.3.7.8.9 HxCDF
.3.4.8.7.8 HxCDF
l.2.3.4.8.7.8-HpCDF
,2.3.4. 7.8.9-HpCDF
XDF
relcachlofobipheny1
lexachlorobiphenyl
teplacMoroblphenyf
tofuo(a)pyrene
laruo(b)fluoranlhann
lls(2-fllhvfhexyl)phlhalalfl
Carbon lelrachloride
)lb»in2(»,h)anlhiacen«
>l(n)octyl phlhalale
<«plachlor
lexachtorotMiuene
taxachlorobutadlene
lexachlorocyclopenladiene
lexachtorophorve
ideno(1 .2.3-cd)pyi»ne
\n1imony
tramlc
larlum x
I«fy1llum '
Cadmium
Chromium (hexavalnnl)
ead
tatcuiy
licks!
.elenium
.irver
hallium
me
DIOXIN TEQ
ORGANICS TOTAL (non-dio»m)
INORGANICS TOTAI
SUBAREA TOTAL

Subaipa

Etavg
El avg
E1 avg
Elavg
El avg
Etavg
E1 avg
Etavg
E1 avg
El avg
El avg
E1 avg
Elavg
El avg
E1 avg
El avg
E 1 avg
El avg
El avg
Elavg
E1 avg
El avg
E1 avg
El avg
El avg
E1 avg
Elavg
Etavg
El avg
El avg
E1 avg
Elavg
E1 avg
Elavg
E1 avg
Elavg
Elavg
E1 avg
E1 avg
E1 avg
Et avg
E1 avg
E1 avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
E1 avg
Soil
tnqflslinn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
99E 11
1 9E-08
NT
2 BE 11
22E 11
2 7E-08
29E 07
1 4E-10
1 2E-07
NT
61E 09
3 2E 07
1 7E 09
50E 11
28E 09
1 3E 09
NT
3 7E-06
48E-10
36E 07
1 BE 09
6 3E 06
2 1E-10
NT
46E-07
1 IE 05
1 IE-OS
Soil
Deimal
Conlarl
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E 10
2 IE -08
NT
3 IE 11
24E 11
29E 08
32E 07
1 5E 10
1 3E-07
NT
1 1E-09
5 7E 08
30E-10
9 IE 12
50E-10
24E-10
NT
66E 07
B7E 11
85E 08
32E 10
1 1E 06
3BE-11
NT
50E-07
1 9E 06
2 4E 06
Bi-nf
Inqnslinn
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 9E 04
2 BE 09
NT
2 1E 04
5 9E 08
2 7E 07
1 9E 07
34E 10
90E-04
NT
7 1E 08
1 6E 06
2 IE 09
53E 11
3 IE 08
6 7E 09
- NT
4 3E 06
1 OE 08
2 OE 06
72E 08
1 9E 04
7 3E-IO
NT
1 3E 03
20E 04
1 5E 03
Pmk
Inqpslinn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
52E 06
46E-10
NT
5 7E 06
1 8E 09
1 OE 07
92E OB
1 6E 10
2 3E-05
NT
1 2E 08
23E 07
40E 09
1 9E 11
58E 10
3 7E 09
NT
60E 06
1 9E OB
2 1E-05
6 7E 10
3 3E 04
79E 11
NT
34E-05
36E 04
3 9E 04
Oi" km
ltii|fsliiin
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
23E 13
2 BE 12
NT
38E 13
4 BE 13
26E 10
25E 10
4 1E 13
49E-08
NT
1 3E 10
1 3E 07
2 IE 12
10E-12
34E 09
59E-11
NT
1 6E 06
4 IE-It
94E 07
1 1E 11
9 2E 05
9 7E-11
NT
49E 08
95E 05
95E 05
OllK'l
Piiillliy
hiqpslnm
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
83E 14
7 7E-13
NT
1 OE-13
t 3E 13
7 IE 11
68E 11
1 IE 13
1 3E 08
NT
34E-11
3 4E 08
5BE-13
28E 13
9 IE 10
1 6E-11
NT
4 3E 07
1 IE-It
25E 07
3 1E 12
25E 05
7 6E 11
NT
1 3E 08
26E 05
2 6E 05
Eqq
Inqpshnn
HO
HJ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 10
1 6E-09
NT
22E-10
28E-10
1 5E 07
1 4E 07
24E-10
2 BE -05
NT
6 BE 10
7 5E-08
78E-10
56E-13
37E-11
44E 11
NT
62E08
30E 11
4 3E 07
1 OE 10
4 2E 05
45E 11
NT
2 BE 05
43E 05
7 1E 05
TOTAL
MEAT «.
EGG
NGESIION
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
20E44
4 BE -09
NT
2 2E-04
8 IE 08
52E-07
43E4)7
74E-10
95E-04
NT
B4E 08
2 IE 06
70E-09
74E-11
36E08
1 1E-08
NT
1 2E 05
2 9E 08
24E 05
7 3E 08
6 BE 04
9 7E 10
NT
1 4E 03
72E 04
2 1E-03
Milk
Inqpslittn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 04
2 7E-09
NT
1 9E04
5 3E OS
2 4E-07
1 8E-07
31E-10
8 1E-04
NT
20E 08
1 4E 07
1 4E-08
14E 13
5 4E 09
52E-09
NT
1 6E 05
49E 09
85E 06
1 4E 06
2 7E 05
5 4E 10
NT
1 2E 03
5 3E 05
1 2E 03
c)_
liiqf»;linn
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
15E-05
24E-10
NT
1 6E 05
4 6E-09
2 tE-08
15E-08
27E-11
7 OE-05
NT
1 BE 09
12E-08
t 2E-09
12E-14
47E-10
46E-10
NT
1 4E 06
43E-10
74E 07
1 2E 07
2 3E 06
4 7E 11
NT
1 OE 04
46E 06
1 1F 04
Milk
Inqpslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
19E-05
30E-10
NT
2 OE-05
5 BE 09
2 7E 08
t 9E-08
3«E-11
8 BE -OS
NT
22E-09
1 5E-08
16E 09
1 5E-14
59E-10
57E-10
NT
1 7E 06
53E 10
92E 07
1 5E 07
29E 06
59E 11
NT
1 3E 04
5 7E 06
1 3F 04
Yogufl
Inqeslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
56E-06
8.9E-1t
NT
81E-06
1 7E-09
80E-09
5 BE 09
10E-11
28E-05
NT
86E 10
4 BE -09
47E 10
44E 15
18E 10
1 7E-10
NT
51E07
16E 10
2 BE 07
45E 08
BBE 07
1 BF 11
NT
3 BE 05
1 7E 06
4 OF OS
Cie.im
Inqptlmn
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
37E06
60E-11
NT
4 IE 06
12E09
53E09
3 9E 09
6 BE 12
t BE 05
NT
44E 10
3 IE 09
3 1E 10
30E 15
1 2E 10
1 IF 10
NT
34E 07
1 IE 10
1 BE 07
30E 08
59E 07
t ?F 11
NT
1 SE 05
1 1E 06
7 ?F 05
Bullpi
Inqpslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
56E 06
89E It
NT
6 IE 06
1 7E 09
80E 09
5 BE 09
1 OE 11
26E-05
NT
66E 10
4 6E 09
4 7E 10
44E 15
1 BE 10
1 7E 10
NT
5 1E 07
1 6E 10
2 BE 07
45E 08
8 BE 07
1 BF 11
NT
3 BE 05
1 7F 06
4 OF 05
olum» V. Apfwndii V-17
-------
ABLE t Avq A Miqh cntl Crim rr RI-.V.. A
                                     NONCARCINOGFNIC HAZARD QUOTIENTS
Chemical
3.78 TCDD
2.3 7.8 PeCDD
2.3.4.7.8 HxCDD
2.3.6.7,8 HxCDD
2.3.7,8.9 HxCDO
2.3.4.8.7.8-HpCDO
COD
! 3.7.8TCDF
2.3.7.8 PeCDF
3.4.7.8PeCDF
2.3.4.7.8 HxCDF
2.3.6.7.8-H*CDF
2 3.7.8,9-HxCDF
3,4,6.7.8 HxCDF
2.3.4.8.7.8-HpCDF
2.3,4,7.8,9 HpCDF
:DF
ilrachloroblphenyl
ixachlofoblphenyt
ipfachlorobiphenyl
nio(»)pytene
f fUo(b)nuoranfhene
* i(2-ethylhexy1)phihalal«
I rbon lelrachloride
< )«fu(a,h)anlhiacena
= 'n)oclyt phlhalale
: plachlof
xachlofobenzena
KBchlorobuladtone
xachlorocyclopenladiene
»a.chlorophene
nno(1 ,2,3-cd)pyrene
limony
ienic
lum
•ytlium v
dmlum
lomium (hexavalenl)
id
icury
knl
enium
el
iltium
i
OXIN TEQ
3GANICS TOTAL (non dio«m)
ORGANICS TOTAL
SUBAREA TOTAL
Subafea
Elavg
Elavg
El avg
Et avg
Et avg
E1 avg
El avg
Et avg
Et avg
Elavg
Etavg
Etavg
Etavg
El avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
E1 avg
El avg
Et avg
El avg
E1 avg
El avg
E1avg
E1 avg
Elavg
Et avg
El avg
Et avg
Elavg
Et avg
Et avg
Etavg
Et avg
El avg
Etavg
E1 avg
El avg
Elavg
E 1 avq
E 1 avg
E1 avg
E1 avg
El avg
El avp
TOTAL
DAIRY
PRODUCT
INGESTION
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 2E4J4
35E-09
NT
24E-04
68E-08
3 1E-07
2 3E 07
40E 10
1 OE-03
NT
26E-08
1 8E 07
1 8E-08
1 7E-13
7 OE-09
6 7E-09
NT
20E-05
6 3E-09
1 IE-OS
1 8E 06
35E 05
69E-10
NT
1 5E-03
6 BE 05
1 6E 03
Eipospd
Pioduce
Ingnshnn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
40E06
1 BE-06
NT
7 7E 07
1 4E 10
93E-09
1 6E-07
30E-11
2 3E-07
NT
3 5E-08
2 5E-07
53E 09
97E-12
9 7E-08
2 76-10
NT
1 OE 04
2 1E 09
44E 07
25E 08
64E 07
23E 08
NT
70E 06
1 OE 04
1 1E-04
Piolorled
Pioduce
Inqnstion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 4E 12
1 5E 06
NT
1 4E 13
1 2E 12
76E 09
1 4E 07
25E 11
1 3E-09
NT
1 9E 08
82E 08
2 3E 09
1 3E-12
49E 08
B3E-11
NT
86E 05
1 5E 09
28E 07
t BE 08
26E OB
2 OE-OB
NT
1 7E 06
86E 05
8 BE 05
Lealy
Puiduce
Inqpstion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
8 BE 05
39E 07
NT
1 7E 05
3 OE-09
1 1E-08
4 IE 08
20E-11
1 3E-07
NT
40E-08
23E 07
7 4E 09
69E 12
6 9E 08
1 4E-10
NT
1 3E-04
5 BE 10
1 4E 07
2 1E 08
36E 07
8 7E 09
NT
1 IE 04
1 3E 04
2 4E 04
Rool
Ptoducp
Inqrshon
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
49E 12
4 2E-07
NT
35E 09
7 1E 11
42E-07
51E 07
70E 10
1 3E4>6
NT
44E 11
58E-11
40E-12
21E 16
1 7E-10
1 OE-14
NT
32E 08
73E 14
79E.I1
4 2E 11
1 BE 12
58E t2
NT
2 7E 06
3 ?E 08
2 7E 06
Fiuil
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 4E-06
1 SE-Ofl
NT
65E 07
1 2E 10
79E-09
1 4E-07
26E-11
2 OE-07
NT
3 OE 08
2 1E 07
46E-09
83E 12
8 3E-08
2 3E-10
NT
8 7E 05
1 8E09
3 BE 07
2 1E 08
54E 07
?OE 08
NT
59E 06
8 BE 05
94E 05
Funl
Inqnstion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E-t2
3 6tf-06
NT
34E 13
2 9E-12
1BE-08
3 3E-07
60E 11
3 OE-09
NT
45E-08
2 OE-07
55E-09
30E-12
1 2E-07
20E-10
NT
2 1E 04
3 7E 09
6 7E 07
4 3E 08
62E 08
4 7E 08
NT
40E 06
2 IE 04
2 1E 04
TOTAL
FRUIT S
PRODUCE
INGESTION
HO
NT
NT
, NT
' NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
96E-05
93E-06
NT
t 8E-OS
33E-09
4 8E-07
1 3E-06
86E-10
19E-06
NT
1 7E 07
9 7E-07
2 5E-08
29E-1t
4 1E 07
93E-10
NT
6 1E-04
9 7E-09
1 9E 06
1 3E 07
1 6E 06
1 2E 07
NT
1 3E 04
6 IE 04
7 4E-04
RIVPI
WnlPi
loqnsllon
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E-15
t OE-12
NT
t9E 16
1 5E-16
4 9E-13
2 3E-12
94E-16
1 3E-t2
NT
38E-13
t IE-It
97E-14
77E-16
29E 13
1 7E-14
NT
24E 10
20E 14
95E 12
1 IE 13
6 1E 11
1 3F 14
NT
5 1E 12
3 2E 10
32E 10
RIVPI
Walci
Dpimal
Contact
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E-11
23E-11
NT
52E-t2
24E-13
81E-10
7 7E-10
74E-t3
t 3E-08
NT
14E 13
40E 12
35E-14
2 BE 16
1 1E-13
62E-15
NT
86E 11
72E 15
35E 12
39E 14
2 2E 11
4 BE 15
NT
1 5F 08
1 ?E 10
i sr ns
Lake
Walei
Inqeslion
HO
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
tIA
NA
HA
Lake
Walpt
Dermal
Conlacl
HO
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
HA
HA
TOTAL
HI
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 IE 04
93E-06
NT
4 7E-04
t 3E-07
1 4E-06
26E06
23E09
2 OE-03
NT
29E 07
36E 06
5 2E 08
1 6E 10
46E 07
20E 08
NT
64E 04
46E 08
3 BE 05
2 OE 06
7?E 04
t ?F 07
NT
IDE 03
1 4F 03
4 4F 01
  im« V AppendwV-17
-------
   1 Avq f. Hiqh
                                    CARCINOGENIC RISKS



Chemical

3 7,8 TCDD
2,3,7.8 PeC DO
2,3.4 7.8 HxCDD
2.3,6.7,8 HxCDD
2,3.7.8.9 HxC DO
2,3,4,6.7,8 HpCDD
ODD
3.7,8-TCDF
2,3.7,8-P«CDF
3.4,7.8-PeCDF
2,3.4.7.8 HxCDF
2.3.6.7.8-HxCDF
2.3.7.8.9 HxCDF
3.^.6. 7.8- HxCDF
2.3.4.8.7.8-HpCDF
2.3.4.7.8,9-HpCDF
CDF
jlrachlotobiphenyl
»xachloroblpheny1
tplachlotobiphenyl
inzo(a)pyiene
mzo(b)f1uoranlhene
s(2 eHiy1l.exyl)phlhalaie
lib* n lelrachlotide
beaz(a.h)anlhracene
(n)octyl phlhalale
iplacnlof
>»achlurobf»nzene
ixachlorobuladtene
ixachlorocyclopentadiene
ixachloiophene
leno( 1 .2 ,3-cd)pytene
sonic

'*V.m ^
rt
iromlum (hexavalenl)
ad

if cury
:kel


vef
1C
IOXIN TEQ
'RGANICS TOTAL (non-dio«m)
IORGANICS TOTAL
SUBAREA TOTAL



Suhaipa

E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
Et hi end
E 1 hi end
E1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
El hi end
E1 hi end
El hi end
El hi end
E 1 hi end
E t hi end
El hi end
El hi end
E 1 hi end
E1 hi end
E t hi end
E1 hi end
E 1 hi end
Et hi end
El hi end
E 1 hi end
E1 hi end
E t hi end
E1 hi end
Et hi end
E 1 hi end
E 1 hi end
El hi end
El hi end
El hi end
E1 hi end
E 1 hi end
E 1 hi end


Soil
Inqeslion
Risk
1 9E 11
4 7E 11
1 IE 11
1 9E 11
1 2E-11
1 4E 11
67E-12
1 7E-11
28E-11
34E-10
1 7E-10
1 6E 10
36E-11
1 BE 10
1 1E 10
1 4E 11
2 1E 11
1 OE 12
1 7E 12
1 7E 12
2 3E 11
96E 12
1 6E 14
99E 13
55E-11
NT
29E-14
20E-11
26E-12
NT
NT
62E-12
NT
95E-11
NT
62E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 09
1 2E-10
95E-11
1 4E 09

Soil
Dermal
Contact
Risk
1 OE 11
26E 11
5 BE 12
1 OE 11
66E 12
75E 12
36E 12
94E-12
15E 11
19E-10
90E 11
BSE 11
20E 11
96E 11
5 BE 11
74E 12
1 IE 11
5 7E 13
92E 13
90E 13
2SE 11
1 OE 11
1 7E 14
1 1E-12
60E-11
NT
3 1E 14
2 1E-11
28E-12
NT
NT
6BE-12
NT
1 7E-11
NT
1 1E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
65E-10
1 3E 10
1 7E 11
79E-10


BPP(
Inqpsllon
Risk
3 IE 08
26E 07
35E 08
94E 09
1 3E 08
1 OE 08
1 8E 07
97E 09
2 3E-08
1 3E-06
1 5E-07
2 7E 07
6 1E 08
1 8E 07
1 4E 08
29E 09
1 5E 08
34E 10
22E 10
6 IE 09
4 BE 07
2 BE 08
7 7E 08
36E 13
7 2E-08
NT
1 9E 10
49E 10
4 3E-12
NT
NT
66E-09
NT
1 2E-09
NT
1 6E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
26E 06
67E 07
1 2E 09
3 2E 06


Pork
Inqestion
Risk
3 7E 09
2 3E 08
30E 09
1 2E 09
1 4E 09
8 7E 10
1 5E 08
1 OE-09
2 IE 09
1 2E 07
1 7E 08
25E 08
58E 09
1 BE 08
1 7E-09
4 IE-ID
1 3E 09
1 2E 10
76E 11
54E 10
1 5E OB
1 OE 09
2 3E 09
66E 14
3 BE 09
NT
64E 12
2 1E-10
23E-12
NT
NT
39E-10
NT
2 OE-10
NT
65E-13
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 4E 07
2 3E 08
20E 10
2 6E 07


dm kon
Inqpslion
Risk
1 6E 10
3 7E 10
4 OE 11
6 IE 11
5 IE 11
93E 12
65E 12
3 1E 11
38E 11
2 OE-09
73E-10
5 BE 10
1 3E-10
59E-10
8 1E-11
25E-11
7 7E 12
1 2E-11
70E-12
7 IE 12
78E 13
40E-13
82E-17
33E 16
70E 12
NT
1 4E-15
42E 13
49E-15
NT
NT
72E-13
NT
83E-11
NT
28E-14
NT
NT
NT
NT
NT
NT
NT
NT
NT
49E-09
35E 11
83E 11
50E 09

Olhpi
Poultry
Inqpshnn
Risk
4 3E 11
1 OE-10
1 1E-11
1 7E 11
1 4E 11
2 5E-12
1 BE 12
84E 12
1 OE 11
55E-10
20E 10
1 6E 10
3 7E 11
1 6E 10
22E 11
69E 12
2 1E-12
33E 12
1 9E 12
20E 12
2 IE 13
1 1E 13
22E 17
89E 17
1 9E-12
NT
38E-16
1 2E-13
1 3E-15
NT
NT
20E-13
NT
23E-11
NT
76E-15
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E 09
97E 12
2 3E 11
1 4E 09


Eqg
Inqeslton
Risk
7 IE 11
t 7E 10
1 BE 11
2BE 11
23E 11
42E 12
30E 12
1 4E 11
1 7E-11
9 IE 10
33E 10
2 7E 10
6 1E-11
2 7E-10
37E-11
1 2E-11
35E 12
54E 12
32E 12
33E 12
32E 10
1 6E 10
34E 14
1 3E 13
29E-09
NT
57E-13
1 BE 10
20E-12
NT
NT
3 OE-10
NT
3.6E-11
NT
1 1E-14
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 2E 09
39E 09
36E 11
6 1E-09
TOTAL
MEAT «,
EGG
INOESTION
RISK
35E 08
2 BE 07
3 BE 08
1 1E 08
1 4E 08
1 1E 08
2 OE 07
1 IE 08
2 5E 08
1 4E-06
1 6E 07
2 9E 07
6 7E 08
2 OE-07
1 6E 08
3 3E 09
t 7E-08
49E 10
31E-10
67E-09
5 OE-07
30E-OB
7 9E 08
56E-13
7 BE -08
NT
2 OE-10
67E-10
87E-12
NT
NT
73E-09
NT
16E-09
NT
23E-12
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 BE 06
70E 07
1 6E 09
35E 06


Milk
Inqpslion
Risk
63E 09
53E 08
7 2E 09
1 9E-09
2 6E 09
2 IE 09
3 8E 08
2 OE 09
4 6E 09
2 7E 07
3 OE 08
5 5E 08
1 2E-08
3 6E 08
2 9E 09
59E-10
3 2E 09
7 IE 11
45E 11
1 3E 09
5 2E-07
3 OE 08
8 2E-08
43E-13
7 7E-08
NT
2 OE-10
54E-10
4BE-12
NT
NT
71E-09
NT
1 3E-10
NT
50E-15
NT
NT
NT
NT
NT
NT
NT
NT
NT
52E 07
7 1E 07
1 3E 10
1 ?F 06


Clippse
Inqpslion
Risk
65E 09
55E 08
7 4E 09
2 OE-09
2 7E 09
2 2E-09
3 9E-08
2 OE-09
4 8E-09
2 8E-07
3 IE-OS
5 6E-08
1 3E-OB
3 7E-08
3 OE-09
6 1E-10
3 3E-09
73E-11
4 7E-11
1 3EO9
36E48
2 1E 09
29E-14
53E-09
NT
1 4E-11
37E-11
33E-13
NT
NT
49E-10
NT
8 7E-12
NT
35E-16
NT
NT
NT
NT
NT
NT
NT
NT
NT
5 4E 07
5 IE 08
8 7E 12
59F 07

Milk
Dpsserts
Inqpslion
Risk
3 6E 09
3 OE 08
4 IE 09
1 IE 09
15E-09
1 2E-09
2 IE 08
1 1E-09
26E09
1 5E 07
1 7E-08
3 IE-OS
70E09
2 OE-08
16E-09
33E-10
1 8E-09
40E-11
26E-11
7 1E-10
4 5E-08
26E-09
71E-09
3 7E-14
67E-09
NT
18E-11
47E-11
4 1E-13
NT
NT
62E-10
NT
1 1E-11
NT
4 4E-16
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E 07
6 3E 08
1 IE 11
TRF 07


Yoguil
Inqeslion
Risk
1 6E-10
1 4E-09
1 BE 10
49E 11
67E 11
53E-11
96E-10
50E-11
1 2E-10
6 BE -09
7 6E-10
1 4E 09
32E-10
92E 10
73E-11
15E-11
80E-11
1 8E-12
1 1E-12
32E tl
1 3E-08
77E 10
2 1E-09
1 1E-14
2 OE-09
NT
52E-12
1 4E-t1
12E-13
NT
NT
1 8E-10
NT
32E-12
NT
1 3E-16
NT
NT
NT
NT
NT
NT
Nl
m
NT
1 3E 08
1 8E 08
32F t?
i IF m


Cieam
Inqeslion
Risk
24E 09
2 IE 08
2 BE 09
74E 10
10E 09
8 OE-10
1SE08
76E 10
1 BE 09
1 OE-07
1 2E-08
2 IE 08
4 BE 09
t 4E 08
1 IE 09
23E 10
12E09
27E 11
1 7E-11
48E-10
1 6E 08
93E-10
25E 09
1 3E 14
24E-09
NT
63E 12
1 7E-11
1 5E-13
NT
NT
22E-10
NT
39E-12
NT
1 5E-16
NT
NT
NT
NT
NT
NT
NT
NT
fIT
20E 07
2 IF 08
39F 12
7 ?f 07


Bullet
Inqeslinn
Risk
1 IE 08
9 IE 08
1 2E 08
3 3E 09
4 5E 09
3 6E 09
6 5E 08
34E 09
79E 09
4 6E 07
5 IE 08
9 3E 08
2 IE 08
62E08
49E 09
1 OE 09
S4E 09
1 2E 10
7 7E 11
2 1E 09
22E 08
1 3E 09
34E 09
1 BE 14
3 2E-09
NT
BSE 12
22E 11
20E 13
NT
NT
30E 10
NT
53E 12
NT
2 1E-18
NT
NT
NT
NT
NT
NT
NT
NT
NT
90E 07
32E 08
53F 12
1 IF 07
ume V. Appendix V-17
-------
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iuJUJUJUJWWUJUJiIiuJUJujuJuJUJUJujuJUJuau^                                             UJUJUJUJ
ORGANICS TOTAL (
INORGANICS TOTAL
-------
NONCARCINOGENIC HAZARD QUOTIENTS
TOTAL

Chemical

.3.7,8 TCDD
,2,3,7,8-PeCDD
2.3.4.7.8 H»C DO
2.38,7,^H«CDD
2.3,7.8.9-H«CDD
2.3,4.6.7,8-HpCDD
COO
3.7,8-TCDF
2.3.7.8-PeCDF
3.4.7.8-PeCDF
2.3.4, 7.8- HxC Of
2.3,6.7.8-HxCDF
2.3.7.8,9-H«COF
3.4.6,7,8-HxCDF
2.3.4,6,7.8-HpCDF
2.3,4. 7.8.9-HpCDF
CDF
tttachlorobiphenyl
ixachloroblphenyl
iplachloioblpbenyl
iruo{a)pyran«
inzo(b)f)uoranthene
!(2-efhy1hexy1)phlhal3le
irbon latrachloride
banz(a.h)anthracene
(n)octyt phlhalale
iptachlor
utachtofobanzema
ixacMoiobutadlene
ixachkxocyclofmnladiene
ixachlorophena
l«no( 1 .2.3-cd)pyrene
llmony
sonic
rium
rylllum »;
dmlum
romlum (haxaralenl)
id
rcu'V
Knl
lenium
iet
^Hiurn
c
OXIN TEQ
RGANICS TOTAl (non-dioim)
ORGANICS TOTAL
SUBAREA TOTAL

Subaiea

E t hi end
E 1 hi end
E 1 hi end
E 1 hi end
E t hi end
El hi and
El hi and
El hi end
El hi and
E1 hi end
El hi and
Et hi and
E 1 hi end
E 1 hi and
E 1 hi end
E 1 hi end
E t hi end
E 1 hi end
E t hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E t hi end
El hi end
El hi end
E t hi and
El hi end
El hi end
El hi end
El Mend
El hi end
El hi end
E1 hi end
E1 hi end
E 1 hi end
E 1 hi end
El hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E 1 hi end
E1 hi end
E 1 hi end
E 1 hi end
DAIRY
PRODUCT
INGESTION
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
84E 04
1 OE^>8
NT
7 OE-04
20E-07
9 2E-07
8 7E-07
1 2E-09
3DE-03
NT
76E-08
5 3E-07
5 4E-08
5 1E-13
2 OE-08
2 OE-08
NT
59E 05
1 8E OS
3 2E-05
52E 06
1 OE 04
2 OE 09
NT
4 4E 03
2 OE 04
46E 03
Expound
Pioduce
Inqoslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 OE^»
4 5E-O6
NT
1 9E 06
34E-10
2 3E-08
40E-07
75E-11
5 BE -07
NT
B7E4>8
82E07
1 3E-08
24E-11
2 4E 07
69E-10
NT
25E-04
5 3E 09
1 IE 06
6 IE 08
1 6E 06
59E 08
NT
1 7E-05
26E 04
2 BE 04
Pinlpi Ipd
Pioduce
Inqoslion
HO
' NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
3 4E-12
38E-06
NT
36E 13
3 1E 12
1 9E-08
34E 07
63E-11
3 1E-09
NT
46E08
20E 07
5 7E 09
3 1E-12
1 2E 07
2 1E-10
NT
2 IE 04
3 BE 09
69E 07
4 4E 08
6 4E 08
4 9E 08
NT
4 1E 06
2 IE 04
2 2E 04
(paly
Pioduce
Inqnslinn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E^M
9 7E-07
NT
42E-05
74E 09
26E 08
1 OE-07
5 1E-11
3 3E-07
NT
99E 08
5 7E 07
1 8E 08
1 7E 11
1 7E 07
3 4E-10
NT
32E 04
1 4E 09
35E 07
5 IE 08
89E 07
2 2E 08
NT
26E 04
32E 04
5 8E 04
Ronl
Pinducp
Inqpsfmn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-11
1 1E-06
NT
88E-09
18E-10
1 1E-06
1 3E 06
1 7E-O9
32E-06
NT
1 1E-10
15E-10
10E-11
52E-16
43E-10
26E-14
NT
BOE 08
1 8E-13
20E 10
t 1E-10
4 BE 12
1 5E 11
NT
67E 06
8 IE 08
6 ?E 06
Fxpnsf'd
flllll
I'tqnMion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
85E06
3 BE -06
NT
16E-06
29E-10
2 OEM
3 4E-07
64E 11
49E-07
NT
7 4E 08
5 3E-07
1 1E-08
2 IE 11
2 1E 07
58E-10
NT
2 2E 04
45E 09
94E 07
5 2E 08
1 3E 06
50E 08
NT
1 5E 05
2 2E 04
2 3E 04
Piolprlod
Fnul
Inqnstion
HO
NT
NT
NT
NT ,
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
82E-12
92F.-06
NT
86E-13
74E-12
4 8E-08
82E-07
1 5E-10
76E-09
NT
1 1E-07
4 9E-07
1 4E 08
76E-12
2 9E-07
50E-10
NT
5 2E 04
93E 09
1 7E 06
1 IE 07
1 6E 07
1 2E 07
NT
1 OE 05
5 2E 04
53E 04
TOTAL
FRUIT A
PRODUCE
INGESTION
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 4E-04
23E-05
NT
45E-05
82E-09
12E-06
33E-08
22E-09
4 7E-06
NT
4 2E-07
24E-06
6 3E 08
73E-11
10E-06
23E-09
NT
1 5E-03
24E-08
4 BE 06
32E 07
40E 06
30E 07
NT
32E 04
1 5E 03
1 8E-03

Rivnr
Walpi
Inqi'Slton
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E-15
1 OE-12
NT
19E-18
1 SE-16
49E-13
2 3E-12
94E-16
1 3E-12
NT
38E-13
1 1E-11
97E-14
77E-18
29E-13
1 7E-14
NT
24E-10
20E 14
95E 12
1 IE 13
6 1E-11
1 3E 14
NT
5 1E-12
32E 10
3 ?F 10
Rtvrt
Walfl
D<>irn;il
Conlacl
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
28E-11
23E-11
NT
52E-12
2 4E-13
8 1E-10
7 7E-10
7 4E-13
1 3E-08
NT
1 4E-13
4 OE-12
3SE-14
2 8E-16
1 1E-13
62E-15
NT
86E-11
72E 15
35E 12
39E 14
2 2E 11
48F.15
NT
1 5E 08
1 2E 10
1 5f Ofl

Lake
Walni
Inqnslinn
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
nn
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
tIA
NA
Lake
Walpi
Dermal
Conlacl
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
rw^
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
UA
NA
NA
UA
NA


TOTAL
HI
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
n i
NT
NT
NT
NT
NT
NT
NT
rt i
NT
n i
1 4E 03
2 3E-05
NT
1 3E-03
36E-07
34E-06
55E06
53E 09
5 4E-03
NT
72E 07
86E-06
1 4E-07
32E-10
1 IE 06
5 1E-OB
NT
1 6E 03
1 2E 07
1 OE 04
5 7E 06
1 8F 03
IDF 07
NT
8 1E 03
36F 03
1 ?F 07
ime V. Appendu V-17
-------
rABLF 1  Avq A High pniir.inrpi Ri-.k-, A rinnraiupi HO<. Sulisi'.lpnr P I" .innpi Atlull
           Chemical
          NONCARCINOGENIC HAZARD QUOTIENT0,
            TOTAL
            DAIRY     Enpospd   Pinlprlpd    lp.ily       Rmit     FIIIO'-PI
          PRODUCT   Produce    Ploduce    Pimlurn    Pmiliu P     Fiuil
Suh.Tipa  INGESTION  IngnOion   Ingnslmn   \nqf,linn   Inqrslin'i   InqpslHi
              HO        HO        HO        HO         HO         HO
             TOTAL                 RIVPI
Prolcrlpd   FRUIT A      RIVPI      WalPi
  Fiuil     PRODUCE   Wal"i     Dfiinal
Inqcilion IMGFSTION  lriqf-,lion    Conlst I
   HQ        HQ         HO        HO
             Lakfl
  L.ike      Watni
 Wiilpi     Dermal
Inqpslion    Corilacl     TOTAL
  HO         HO        HI
 NA = Not applicable
 NT * No Joxlcrty information
 HO * Hazard quolinnl
 HI -Hazard Index
 TEQ - TCDO equivalents
       V. Appendu V-17
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Chemical
>.. 3.7.8 TCDD
.2.3.7.8-PeCDD
.2,3.4.7.8 HxCDD
.2.3.6,7.8 HxCDD
.2 3.7 8 9-HxCDD
,2.3.4.6.7,8-HpCOO
X;DD
'.3.7,8-TCDF
1.2.3,7.8-PeCDF
'.3.4.7.8-PeCDF
,2.3,4.7.8-HxCDF
.2.3.6 7 8-HxCDF

,2.3.7,8.9-HxCDF
.3 4.8 7,8-HxCDF

,2.3.4.6.7.8-HpCDF
.2,3.4,7.8.9-HpCDF
XTDF
elrachloroblphenrl
lexachlotobiphenyl
leptachlofoblphenyl
•on?o(a)pyrene
>eruo(b)fluoranthene
ils(2-elhyinf>xyt)phlhalale
art. on telrachlorlde
Hben2(a,h)anlhracene
H(n)octy) phlhalata
leplachlof
lexachlofobanzene
lexachlorobuladlene
exachloiocyclopanladiene
exachlorophena
>d0no(1,2,3-cd)pytene
.ntlmony
fsenlc
afium »;
erylllum
admlum
hromlum (hexavaleni)
gad
tercury
ickel
Blenlum
liver
hallium
nc
Subarea
E1
Et
Et
E1
El
El
El
El
El
El
El
El
El
Et
E1
El
E1
Et
El
El
Et
El
E1
E1
El
El
Et
El
El
El
E1
El
El
E1
El
El
El
E1
El
El
E1
El
Et
El
E1
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emls«
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
hi emiss
AVERAGE
Pmleclpd
Produce
Ingoslion
mg/kg d
7 3E 17
25E-16
60E-17
1 9E-16
70E-17
44E-16
57E-15
50E-16
1 1E-15
1 2E-15
1 7E-15
1 6E-15
37E-16
1 BE 15
52E-15
7 1E-16
42E-15
2 1E-13
62E 14
30E-14
35E 12
1 3E 11
1 BE 13
8 7E-09
3 BE 12
2 7E-14
S7E-15
57E-11
13E 10
1 6E-12
1 BE-12
46E-12
35E-11
1 1E-10
75E-10
30E-14
1 1E-10
1 9E-12
24E-10
1 2E-07
1 4E-10
65E-09
42E 10
B4E 12
2 7E 08
DAILY DOSF (ADD) FOR CHFMICAt S WITH fJONCARCINOGFNIC HEALTH EFFECTS
R'vm Like
Lnafy Rool F«po-;prt Pinlorlrd RWPI Watnr Lako W-ilpi
Produce Produce Fruil Frml Walm Dnrmal Waler Dr-rmal
Ingnshon Ingnslion Inqeslmn li.qnslinn Irignslrun Contarl Iriqosfirm Conlarl
mq/kg d mq/kq d mq/kq d rnq/kq d mq'kq rt mq/kq d mg/kg d mq/kg d
36E 14
45E 13
62E-13
16E 13
20E-13
1 OE 11
15E-09
35E-13
20E-12
2 8E-12
1 9E-12
43E-12
10E-12
32E 12
1 1E-11
90E-13
3 BE 10
4 7E 12
BSE 12
27E-10
30E-08
t 5E-08
1 2E-05
22E-09
65E 11
32E-06
1 4E-11
79E-11
38E-I1
1 3E-12
1 9E-10
66E-11
74E-11
32E 10
2 4E-09
16E-I3
16E-10
32E-12
45E-10
1 8E-07
54E-11
33E-09
48E-10
1 2E 10
1 2E-08
1 6E 16
54E 16
32E 16
74E 16
52E 18
33E 15
26E 14
97E 16
26E-15
31E-15
85E 15
60E-15
1 4E-15
69E 15
3 1E-14
42E 15
50E 14
3 7E 12
5 7E-13
34E 12
9 BE 13
35E 11
65E 13
24E 09
16E tt
6 7E 10
34E 13
32E-09
48E-10
46E-11
1 8E-09
1 7E-11
B4E-14
82E-14
1 3E 12
49E-18
40E-13
25E-16
3 1E-13
45E-11
69E-15
1 9E-12
99E 13
6 IE 16
82E 12
4 3E 15
5 1E 14
7 IE 14
23E 14
25E 14
1 IE 12
16E-10
40E-14
23E-13
32E-13
25E-13
5 1E-13
1 2E-13
39E 13
1 5E 12
t 4E-13
4 3E-11
1 1E-12
1 1E-12
30E 11
35E 09
1 6E 09
1 3E 06
2 4E -08
28E-10
34E-07
1 5E 12
1 7E-10
36E-10
47E 12
7 BE- 10
28E-10
1 6E-10
B4E 10
4 2E-09
54E-13
54E-10
1 5E-11
1 3E 09
34E 07
4 7E 10
2 5E 08
1 4E 09
50E 10
79E 08
50E 16
1 7E 15
4 1E-16
1 3E 15
4 BE 16
30E-15
39E 14
34E 15
74E-15
79E-15
1 IE-14
1 1E-14
25E 15
1 2E-14
36E-14
4 BE 15
2BE-14
1 4E-12
42E-13
2 1E-13
2 4E 11
8 BE- It
1 2E-12
5 9E-08
26E-11
1 8E-13
39E-14
39E-10
8 7E 10
1 1E-11
1 2E-11
3 1E-11
24E-10
7BE-10
5 1E-09
20E-13
7BE-10
1 3E-11
1 6E-09
82E-07
98E-10
44E 08
28E 09
58E-11
1 9E 07
1 1E 20
36E 20
96E 21
3 6E 20
2 5E 20
53E 20
98E-19
6 BE -20
1 BE-19
20E 19
3 IE-19
29E-19
69E 20
3 3E-19
78E-19
1 1E-19
30E-19
2 2E-17
1 BE-17
2 1E-17
35E-18
1 3E-15
4 7E-16
5 7E-15
82E-16
38E-17
68E-19
37E-15
22E-15
61E-17
1 8E-1S
91E-16
7 1E-18
1 5E-14
32E-14
1 8E-17
68E-16
40E-16
24E-14
33E-13
1 9E 15
2 2E-13
25E 15
20E 14
1 8E-14
1 8E 17
49E 17
6 7E 17
1 !E 16
1 7E-16
S6E-16
30E-15
1 IE 16
34E-16
48E-16
1 IE-IS
1 OE-15
2 4E-16
1 2E-15
5 7E-15
7 7E-16
7 4E-15"
2 3E-14
56E-14
1 2E-13
4 2E-13
1 8E-12
1 5E-12
53E-14
2 1E-12
38E-13
44E-16
2 4E-12
29E-13
1 9E-14
7 4E-12
22E-12
IDE-IB
22E-15
46E-1S
26E-18
98E-17
58E-17
35E-15
48E-14
2 7E-16
32E-14
36E-16
29E 15
2 7E 15
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
fJA
MM
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
ilume V. Appendix V-1 7
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HOXIN TEQ
iRGANICS TOTAL (non
IORGANICS TOTAL
SUBAREA
                                                                                                                                                                                   1
                                                                                                                                                                                   *
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 I ABLE ? Avq A Hirjli >>iirf C.MH i>i Ri •,)!••, ^ l)i,
                                                     , HO',
Chemical
?.3,7.B TCDD
I,2,3.7.8P»CDO
12347 8-H«CDD
l.2.36.7.8HxCDD
1.2.3 7.89-HxCDD
l.2.3.4.6.7.B-HpCDO
3COO
J.3.7.8-TCDF
1.2.3,7,8-PeCDF
!.3,4,7.8-PeCDF
l.2.3.4.7.8-HxCDF
1 2.3,6.7.8 HxCDF
1 2.3.7.8,9-HxCDF
'. 3.4.6. 7.8-HxCDF
1 2.3,4.6.7.8 HpCDF
1,2.3,4.7,8.9-HpCDF
JCDF
' »lf achtoroblphany)
lexachlocobtphenyl
feplachkxoblphenyl
tanzo(a)pyren«
(er)zo(b)fluofanlb»n»
Carbon lelrachloilde
>lb«fUf>,h)anlhiacen«
)l{n)octyl pblhalate
(eplrchlof
laxachlorobanzvn*
leiachlofobuladlene
lexachlotocyclopentadlene
lenachlcxophene
ideno(1 r2,3-cd)pyinne
tfilimony
\fsenlc
larlum ^
Iflfytlhim
Cadmium
'liromlum (haxavalent)
ead
tercury
licknl
etenlum
ilvei
halllum
me
DIOXIN TEQ
ORGANICS TOTAL (non-droxm)
INORGANICS TOTAL
SUBAREA TOTAL
Subaroa
E1 avg
E1 avg
El avg
El avg
Elavg
E1 avg
Elavg
El sivg
E1avg
El avg
Elavg
E1 avg
E1 avg
Elavg
E1 avg
El avg
E1 avg
Elavg
El avg
El avg
El avg
El avg
El avg
E1 avg
Elavg
Elavg
Elavg
El avg
Etavg
Elavg
Elavg
Elavg
Elavg
Elavg
El avg
Elavg
Elavg
E1 avg
El avg
Etavg
E1 avg
El avg
El avg
El avg
El avg
Elavg
Elavg
Elavg
E1 avq
CARCINOGENIC RISKS
TOTAL
DAIRY E«posed Prnlecled
PRODUCT Pioduce Produce
INGESTION Inqeslmn Iriqeslirm
RISK Risk Risk
5 7E 09
4 BE 08
65E 09
t 7E 09
24E 09
19E-09
3 4E-08
18E-09
42E-09
24E-07
27E-08
4 9E 08
1 1E 08
33E 08
26E 09
53E-10
28E 09
64E 11
4 IE 11
1 1E 09
2 BE 07
t 6E 08
44E 08
2 3E 13
42E 08
NT
1 1E-10
29E-10
26E-12
NT
NT
38E-09
NT
68E-11
NT
2 7E-15
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 7E 07
39E-07
68E 11
86E 07
46E 12
39E 11
1 1E 11
3 7E-12
38E 12
1 6E-11
22E-10
65E-12
19E-11
26E-10
4 1E-11
85E-11
1 9E 11
64E-11
23E-11
20E 12
4 7E 11
67E 14
60E 14
1 6E 12
1 8E 10
84E 12
1 BE 10
26E 11
1 4E-11
NT
49E 14
19E 12
40E-13
NT
NT
1 4E-12
NT
2 1E-11
NT
33E-14
NT
NT
NT
NT
NT
NT
NT
NT
NT
66E-10
4 1E-10
2 1E 11
1 3E 09
1 BE 13
46E 13
2 2E-14
7 4E-14
25E 14
1 6E 14
1 BE 14
1 9E 13
2 2E 13
23E-12
66E-13
6 IE 13
1 4E 13
69E 13
1 9E 13
2 4E 14
1 1E-14
2 7E 14
80E 15
2E-I7
50E-1B
79E-18
66E-17
90E-17
99E 16
31E-16
29E 18
68E-17
33E-16
72E-17
92E-18
20E-18
73E-18
S9E-18
70E-18
1 1E-16
42E-17
406-19
36E-17
26E-18
NT
1 3E-19
25E 16
14E-17
NT
NT
28E-17
NT
23E-15
NT
87E-18
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E 15
76E 16
2 3E 15
56E 15
River
Water
Deirnal
Conlacl
Risk
1 2E 13
22E 13
6 1E-14
1 1E-13
I6E 13
53E-14
2 4E 14
1 IE 13
1 7E-13
24E 12
1 1E-12
10E-12
24E-13
1 1E-12
52E-13
67E-14
49E-14
76E-15
1 8E-14
40E-14
13E-13
57E-14
1 3E-15
34E-16
65E-13
NT
84E-17
1 7E-13
1 9E-15
NT
NT
68E-14
NT
33E-18
NT
96E-19
NT
NT
NT
NT
NT
NT
NT
NT
NT
75E 12
1 1E 12
34E 16

Lake
Waler
Inqeslinn
Risk
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Lake
Walm
Deininl
Conlarl
Risk
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
NA
NA
Intanl
Bmasl milk TOTAL
Inqeslmn CANCER
Risk RISK
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA

94E09
7 7E 08
1 IE 08
29E 09
3 9E-09
34E09
S9E 08
30E09
72E09
3 9E 07
4 SE 08
8 IE 08
1 8E-08
5 4E 08
48E49
93E-10
57E 09
12E 10
BOE 11
1 BE 09
33E 07
1 9E-08
56E08
27E 10
50E-08
NT
13E 10
55E 10
1 3E-11
NT
NT
rt i
46E-09
NT
5 OE-10
NT
1 2E-12

NT
NT
'NT
NT
NT
NT
NT
NT
7 BE 07
4 8E 07
5 OE 10
1 7F 06
ntume V, Appendix V-17
-------
ABt E 2 Avq A Hiqh pml Cant fi R.-.kv K.
                                           i MOs
                                                          • I ,mm>i Cluld
                                      NONCARCINOGENIC HA7ARD QUOTIENTS


Chemical

3.78 TCDD
2.37.8 PoCDD
2. 3,4. 7.8- HxCDD
2.3.8 7.8-HxCDD
2.37,8.9 HxCDD
2.3,4,87.8-HpCDD
COD
37.8^TCDF
2.3,7.8-peCDF
3.47.8 PaCDF
2.3.4.7,8-HxCDF
2,3.8,7.8-HxCDF
2.3. 7.8.9 HxCDF
3.4 8.7.8- HxC OF
2.34.878-HpCDF
2.3.4. 7.8,9-HpCDF
3DF
ilrachlofoblphanyt
ixachloroblphonyl
iplachlorr>biph0nyt
n?o(a)py(«ne
'fuo(b)nuoranthene
t(2-«(hylha«yl)phthalale
ifbon MrcchkxMe
Mnz(a,h)anttu«cene
n)octy1 phlhalata
plachlot
xochlorobaru'ena
xachtorobutadtorM
XBchtoroeyclopenladlena
xachlorophena
'•no! 1 ,2 ,3-cd)pyiene
llmony
ionic
rlum
ryllium ,
dmlum
romium fhexavalenl)
id
rcury
• el
nnlum
illium
c
OXIN TEQ
3GANICS TOTAL (non-dlo«m)
ORGANICS TOTAL
SUBAREA TOTAL


Suhaiea

Elavg
El avg
Et avg
El avg
El avg
Elavg
Elavg
Elavg
Elavg
Elavg
Elavg
El avg
Elavg
Elavg
E 1 avg
El avg
El avg
El avg
Etavg
E 1 avg
E1 avg
Elavg
El avg
El avg
E1 avg
Elavg
El avg
Elavg
El avg
Elavg
El avg
El avg
El avg
Elavg
El avg
El avg
El avg
El avg
El avg
Et avg
E1 avg
El avg
El avg
E t avq
E1 avg
El avg
Elavg
Et avg
E1 avq


Soil
Inpestmn
HO

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
7 4E-10
1 4E-07
NT
2 IE 10
1 7E-10
2 OE-07
22E-06
1 OE-09
8 9E-07
NT
4 6E-08
24E-06
1 2E-08
38E-10
2 1E-08
99E 09
NT
2 7E-05
36E 09
2 7E 06
1 3E 08
4 7E 05
1 6E-09
NT
3 4E-06
79E 05
8 3E 05

Soil
Dmrnal
Contact
HO

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
86E 11
1 6E-08
NT
25E 11
1 9E 11
23E-08
2 5E 07
1 2E-10
1 OE-07
NT
89E-10
4 6E-08
24E-10
73E 12
40E-10
1 9E-10
NT
5 3E 07
70E 11
52E 08
25E-10
9 IE 07
30E 11
NT
40E 07
1 5E 06
1 9E 06


Bcpl
Inqpslmn
HQ

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E 04
4 3E 09
NT
33E 04
92E 08
42E 07
30E 07
53E-10
1 4E-03
NT
1 1E 07
26E 06
3 3E 09
83E 11
4 BE 08
1 OE 08
NT
6 7E 06
1 6E 08
3 1E06
1 1E 07
2 9E 04
1 IE 09
NT
20E 03
3 IE 04
2 3E 03


Pmk
liiqpslinn
HQ

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 6E 05
1 4E-09
NT
1 BE 05
56E09
32E 07
2 9E 07
5 1E-10
7 3E-05
NT
3 9E 08
7 3E 07
1 3E 08
60E-11
1 BE 09
1 2E 08
NT
1 9E 05
60E 08
65E 05
2 1E 09
1 OE 03
25E 10
NT
1 1E 04
1 IE 03
1 2E 03


Ingnslion
HQ

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E-13
85E-12
NT
1 IE 12
15E 12
79E-10
75E-10
1 2E 12
1 5E-07
NT
38E-10
38E-07
64E-12
31E-12
1 OE-OB
18E-10
NT
4 BE 06
1 2E 10
2 BE 06
34E 11
2 BE 04
29E 10
NT
1 5E 07
2 BE 04
29E 04

Ollipi
Pmiltty
Inqp slinn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-13
14E-12
NT
1 BE-13
24E 13
1 3E 10
1 2E 10
20E-13
2 4E-08
NT
62E-11
6 IE-OS
10E-12
50E-13
16E09
29E-11
NT
7 BE 07
20E 11
46E 07
55E 12
4 5E 05
4 7E 11
NT
2 4E 08
4 6E 05
4 6E 05


Egg
HO
N T
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
34E-10
4 1E-09
NT
S6E-10
7 1E-10
38E-07
37E-07
60E-10
7 1E-05
NT
1 7E-09
1 9E-07
2 OE-09
1 4E-12
93E-11
1 1E-10
NT
1 6E-07
7 7E 11
1 1E 06
26E 10
1 IE 04
1 1E-10
NT
7 2E 05
1 1E 04
1 BE 04
TOTAL
MEAT A
EGG
INGESTION
HQ
MT
N 1
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
31E-04
99E-09
NT
34E-04
99E-08
1 1E-06
96E-07
16E-09
1.5E-03
NT
1 5E-07
39E06
1 BE -08
15E-10
8 1E 08
2 3E 08
NT
3 IE 05
76E 08
73E 05
1 2E 07
1 BE 03
1 BE 09
NT
22E 03
1 9E 03
4 IE 03


Milk
Inqoslion
HQ

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-03
27E-08
NT
1 9E-03
5 3E-07
24E08
18E06
3 1E-09
80E-03
NT
2 OE-07
1 4E-08
1 4E-07
1 4E-12
5 4E-08
5 2E-08
NT
1 6E 04
49E 08
84E 05
1 4E 05
2 7E 04
5 3E 09
NT
1 2E 02
52E 04
t 2E 0?


Chpese
Inqnslion
HO

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
35E05
56E-10
NT
3 BE -05
1 IE-OS
5 OE-08
3 6E-08
63E-11
16E-04
NT
41E-09
2 9E 08
29E-09
2 BE 14
1 1E-09
1 1E-09
NT
32E 08
99E 10
1 7E 08
2 BE 07
55E 06
1 IE 10
NT
24E 04
1 1E 05
25E 04

Milk
Inqnstion
HO

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
7 3E-05
1 2E-09
NT
8 IE-OS
2 3E-08
1 1E-07
7 7E-08
1 3E-10
35E-04
NT
87E 09
8 IE-OS
82E-09
S9E-14
23E-09
23E-09
NT
68E-06
2 IE 09
3 7E-06
60E 07
1 2E 05
2 3E 10
NT
50E 04
2 3E 05
5 IF 04


Yofjurl
Ingnstion
HO

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E-OS
4 9E-10
NT
33E-OS
94E-09
43E-OB
32E-08
S8E-11
I4E-04
NT
36E-09
2 5E-08
25E-09
24E-14
97E 10
93E-10
NT
2 BE -06
8 7E-10
1 5E 06
25E 07
4 BE 06
9 6E-1 1
NT
2 1E 04
94E 06
2 7F 04


Cinam
Inqeslion
HO

NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
NA
MA
NA
MA
MA
MA
MA
MA
MA
MA


Build
Inprslion
HQ

NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
86E06
1 4E-10
NT
95E06
2 7E 09
1 2E 08
90E 09
16E 11
4 IE 05
NT
10E09
7 IE 09
72E 10
69E 15
2 BE 10
2 7E-10
NT
80E 07
25E 10
4 3E 07
70E 08
t 4F 06
2 7E 11

59E 05
2 7E 06
67F 05
ime V. App«ndu V-1 7
-------
'ABLE 2  Avq A High pn
                            ri Rr.ks f. N"i« .inr nc HCK
                                          NONCARCINOGENIC HAZARD QUOTIENTS

Chemical

'.3.7.8-TCDD
1.2.3. 7.8 PeCOD
1,2.3.4.7.8 HxCDD
1, 2.3,6. 7,8-HxCDD
l.2.3,7.8.9-HxCDD
1,2.3,4.6,7,8-HpCDD
I XDO
!.3,7.8 TCDF
1.2.3.7,8 PeCDF
'.3.4.7,8 PeCDF
1.2.3,4.7.8 HxCDF
1.2.3.6, 7.8 HxCDF
i 1.2.3,7.8,9-HxCDF
! 3.4 8,7.8 HxCDF
1.2.3,4.8.7 8 HpCDF
l.2.3.4.7.8.9-HpCDF
X:DF
'alrachlofobiphenyl
taxachloioblphenyl
(eplachloioblphenyt
ten*o(a}pyr«na
l«nzo(b)ttuoranthen«
lls(2-elhylh«xyt)phlhalale
:arbon lelrachlocide
)lbt,nz(a.h)anlhracen9
>l(n)octyl phlhalate
' leplachlof
lexachkMobenzane
laxachlorobutadlene
texachlorocyclopenladien*
lexachlofophene
ideno( t ,2,3-cd)pyrane
knllmcmy
ifssnlc
larlum
lerytllum v
Cadmium
:htomium (hexavalenl)
ead
I tercury

fllflnlum
ilvm
hallium
me
DIOXIN TEO
ORGANICS TOTAL (non dio.in)
INORGANICS TOTAL
SUBAREA TOTAL

Subaiea

El avg
El avg
E1 avg
E1 avg
El avg
El avg
Elavg
El avg
E1 avg
Et avg
Elavg
Elavg
El avg
E1 avg
E1 avg
E1 avg
Et avg
Elavg
El avg
El avg
El avg
El avg
El avg
E1 avg
E1 avg
Elavg
El avg
El avg
Elavg
E1 avg
El avg
Elavg
El avg
Elavg
El avg
El avg
E1 avg
El avg
E1 avg
Et avg
E1 avg
Et avg
Et avg
El avg
Et avq
E 1 avg
E1 avg
Et avg
E 1 avq
TOTAL
DAIRY
PRODUCT
NGESTION
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 BE 03
30E 08
NT
20E 03
5 7E-07
26E-06
1 9E-06
34E09
8 7E-03
NT
2 2E-07
15E06
1 5E-07
1 5E 12
59E08
56E 08
NT
1 7E 04
53E 08
92E OS
t 5E OS
2 9E 04
5 8E 09
NT
1 3E 02
5 7E-04
1 3E 02
Exposed
Produce
Inqeslinn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
74E06
3 3E-06
NT
1 4E 06
25E 10
1 7E 08
30E 07
56E 11
4 3E-07
NT
8 5E 08
4 6E 07
99E-09
1 BE 11
1 BE 07
5 1E-10
NT
1 9E 04
39E 09
82E 07
45E 08
1 2E 06
4 3E 08
NT
1 3E 05
1 9E 04
2 OE-04
P io|p( Ipd
Produce
Intjpslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
25E 12
2 BE 06
NT
26E 13
2 3E 12
1 4E 08
25E 07
46E 11
23E 09
NT
3 4E-08
1 5E 07
42E 09
23E 12
90E 08
1 5E 10
NT
1 6E 04
28E 09
5 1E 07
3 3E 08
4 8E 08
3 6E 08
NT
3 1E 06
1 6E 04
1 6E 04
Ipnly
Produce
IntjeMion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 04
7 5E-07
NT
3 2E 05
5 7E 09
2 OE 08
7 BE 08
39E-11
2 6E-07
NT
7 5E 08
4 4E 07
1 4E 08
1 3E-11
1 3E 07
26E-10
NT
2 4E 04
1 1E 09
2 7E 07
39E 08
68E 0?
1 7E 08
NT
2 OE 04
2 5E 04
45E 04
Riiol
PfrKiucn
Inqp^linn
HO
NT
NT
Nt
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
94E-12
8 1E-07
NT
67E 09
1 4E 10
8 IE 07
9 BE 07
1 3E 09
25E-06
NT
85E-11
1 1E-10
78E-12
40E 16
33E 10
20E-14
NT
6 1E 08
1 4E 13
1 5E 10
8 IE 11
35E 12
t 1E-11
NT
5 1E 06
62E 08
5 IE 06
Fv:;r
InqpMmn
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 BE -05
79E-08
NT
3 4E-O8
6 1E-10
4 1E 08
7 1E-07
1 3E-10
10E-06
NT
1 6E-07
1 1E-06
2 4E 08
43E-11
4 3E 07
1 2E-09
NT
45E 04
95E 09
20E 06
1 1E-07
2 BE 06
1 OE-07
NT
3 IE 05
46E 04
49E 04
Pfolcclpd
Fiinl
ln<|f,lH,n 1
HO
NT
Nt
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E 11
19E-05
NT
1 8E-12
1 6E-11
97E-08
1 7E 06
32E-10
1 6E-08
NT
2 4E 07
10E06
2 9E-08
16E 11
62E 07
1 1E-09
NT
1 IE 03
20E 08
35E 06
2 3E 07
3 3E 07
25E 07
NT
2 1E 05
1 1E 03
1 1E 03
TOTAL
TRUIT A
PRODUCE
NGFSTION
HO
NT
Nt
Nt
Nt
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 9E 04
35E-05
NT
37E-05
87E-09
10E-06
41E-06
19E-09
42E-06
NT
5 7E 07
32E06
8 IE 08
93E 11
15E06
32E-09
NT
2 IE 03
3 7E 08
7 IE 08
4 5E 07
5 1E 06
4 5E 07
NT
2 7E 04
22E 03
2 4E 03
RIVPI
Inqpslitin
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 7E-14
46E-12
NT
89E-18
68E-16
2 3E-12
1 1E-11
4 4E-15
80E-12
NT
1 8E-12
52E-11
45E 13
36E 15
14E-12
80E-14
NT
1 IE 09
93E 14
45E 11
5 1E 13
29E 10
6 1E 14
NT
24E 11
1 5E 09
1 5F 09
W.ilpi
Dflffttal
Contact
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
S2E-11
43E-11
NT
96E-12
44E 13
1 5E-09
1 4E 09
14E-12
2 5E-08
NT
28E-13
74E-12
BSE U
52E-16
20E-13
12E-14
NT
18E 10
1 3E 14
84E 12
73E 14
4 1E 11
8 BE 15
NT
2 BE 08
2 IE 10
? BE 08
Lake
nqpslion
Hb.
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
HA
HA
Lakp
WalPi
Dermal
Contact
HO
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
NA
NA
NA

TOTAL
HI
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 3E 03
35E-05
NT
2 4E 03
6 BE 07
50E06
94E 06
8 IE 09
10E-02
NT
98E07
1 IE 05
2 7E 07
62E 10
1 6E 06
9 2E 08
NT
24E 03
1 7E 07
1 7E 04
1 6E 05
2 IE 03
4 fir 07
NT
1 5F 02
4 7E 03
•> nr n?
 olumn V, Appftndu V-17
-------
                                                                                                             Baa. 'f.Un _Jjj	j_ji.^
|
M
<
OXIN TEO
PANICS TOTAL (non-dic
ORGANICS TOTAL
SUBAREA TO
||3

?

                                                                                   N
                                           !
>     BJ  ai  ^  ^  3*     A
'     ff  8  a  =• «      "
1         9  «   $• 3     -S.
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                                                                                                                                                                       I is  O     "-*  jjj jfc Q
rn rn m m
b — b o
^ o w -~^
Ul U A. NJ
TI rn m m
0 — 0 O
W O» Ol NJ
•n n rn rn
o — o o
-4 fvj OB ^*
^ NJ <-> -*
0—00
-H m rn m
0 — 0 O
-^ ^j a» -^*
TO rn m TO rn m TO TO TO TO TO TO TO TO TO TO TO TO TO TO TO TO rn mmrnmrnmTOmfnTOPn TO TO TO TO TO TO TO TO rn TO rn
333333333333333333333333333 = 33333331333333339

Z ZZ Z ZZZZZTOZTOZTOZZrnTOTOZnirnTOmTOTOTOTOrnTOTOTOTOrnTOfflfflfflfTiTOTOTOrnTOTO

ZZZZZZZZZTOZTOZmZZmrnTOZrnTOTOTOrnrnTOmmTOTOTOmTOTOTOTOTOTOTOTOTOrnrTiTO
* K» KJ UKJ«J» Uft/t KJMl-lUt
^^2rZZZZZZTOZrnZrnZZrnfnrnZrnrnrnrnrnnifnTOTOTOrTiTOniTOTOTOfflTOTOTOniTOTOrnrn

ZZZZZZZZzSzmZmZZmTOmZmTOTOTOmmTOTOTOTOTOTOrnmTOmmTOTOTOTOm
u - o Mo« S*2oSo-o»o*-«,.*.So.ooo*.»
ZZZZZZZZZTOZmZrnZZmmmZTOTO'nmTOTOfnTOTOTOmtTimTOTOTOTOTOTOniTOrnrnrnrn

O O O O) f^> O O-*JfeQ*^OO*<>J-*~<4WO>UAhCBfOtJI *O Ut »*-> PSJ A — O> U
Z^ZZZZZZZTOZTOZrnZZmmmZTOTOTOTO TOmTOrnrnnnTOrnTOnirnTOTOTOTOnrirnrnfnrn rn

^2ZZZZZZZTOZmZmZZniniTOZPhTOfflrttTOTOTOTOTOniTOTOTOTOrnfflTOTOTOTOTOrnrnmm
* - 0 .0. 3^00 	 o-O.— -M.---0-
ZZZZZZZZZniZrnZmZZmniTOZTOfnTOTOTOTOTOTOTOTOTOTOmTOrnTOTOTOTOmTOTOmTOrn
= 33 =3= ^^SSSSSSSgggg^SSgSSSggg
zzzZZZZZZmZmZmZZmmraZmmmSmmmmmmmnrnimmmmmmmmmmmm
„ 0 . ,,00 .U..ft — ....ft.....S.8.....
ZZ ZZ zZZZZrnZTOZmZZmTOmZTOrT. raTOTOTOTOTOTOTOTOTOTOmrTtTOTOTOmTOTOmmmTO
. M o „-- S.S3.S--So«c.«-c..SS«.1»«Slo.>0
zzzzzzzzzmZmZmZZmTOmZmmmmmfSmTOTOmmrnmmmTOmTOTOTOTOTOTOrnTO
-4-^-^-^-^-H-H^— *^-^^Hj^-^-4^^k^k'H;»^^i3ca^JL^*o — oopec>OQ^*o-— Q — OOP
A M o u-t-t (5*355Q_»~*(Zou5a(0aia»~440GOBO u -» KJ (O w-*K*-k*ou»»ouj-*N*io-*w-*»-4-^tn — a>a»c/»M-*'v»
---*-;2ZZZZZTOZmZmZZrnnimZTOnifTimrflTOniTOTOmTOTOTOmmfflmniTOTOmTOTOTOTO
^-.-^--*-t-t-t-*il-t^-»^-*-':i::.i"<^i.6g6^^^5^f:g5g3gsf:gf:::isg3
ii55?5i555i5?552iii55i55$55zI5?z55§5522ZZ55>2
^^ZZZZZZzSzSzmZZmTOmZmTOTOTOmTOTOTOmTOmmmTOmTOTOmmmmTOmmm
— •— •— *— *— .-^-^— <-H- ^'"^'•^"*'''~^Q-__»_kQ^-^^*al*boboooc5-i*O"*Q^(3oo
C w o Jt^lC 3^ooy5o--3o'3cD<2Q»ot-i3oo»0'2o'«a»^
t/i
a-
u
3
at
- O
3 >
? ' « S
3^3 °
'1 0
O
m
no -
73 o a at ci
Is 1 2 a
2. — 01
slf
*" 3 ""
3
'I '
ill
i 3
5"
3
3D rn HI rn n
co w 0 > y
O *r~
5"
M.Ik
Cheese Desserts Yogurt Cream Buttel
on InqeMion tuqestinn Inqestion InqeMion Ingestton
< Risk Risk Risk Risk Risk
-------
<

f
!

<
DIOXIN TEQ E
ORGANICS TOTAL (non-dio«in) E
INORGANICS TOTAL E
SUBAREA TOTAL E
                        =8
                                 l£S I|f 8 fflf f i»
                                 -i|« 3 g  | S |  iff 1  |~
                                              ----
                                                                          -S-2. 2 ff
                                                                          ? 3 2 3
                                                                               >i » Vi at '-* Vi b> a. H   o> » -j '•>• « _

                                                                               « '-« « "(>ama9l>l*«'»«<»»<»«««««««»»««««*.ifl-*K>-k«*at<0tl*-*ai^.^ui-*ui-*jcn*j-**j
                                          Q»   (OM.
          y» -* * at

          
                                                                                                                                                    CD
                     ZZZZZZZZZHiZrnZrnZZHiHiHiZHininimrnmmmHiHiniHinimnimmmnimHi
                                          *   U*   U>      -* O* O»   W-^-^^K>K)^il'*4UI«*-^A-^aiK»n4^mK»-AUK)(OULn


                     ZZZZZZ2ZZrnZrnZniZZmmHiZmmn»nirTirnnimHiHininimmmHimnirnmHinimmm
                                          A   W   W

                                                                                               I (J Jk «*'>^9«*(1)UA^*J^


                                                                                               i m ffl fflHimmrflrnrnmmrri


                                                                                               ia>a)tAQ-4-4Oi-«j--4-*4a)a)
-* (jj KJ «3                        (O   U   -^     —fc U .—   ,


-Timmm   ZZZZZZZZZmZHiZrnZZrnmniz!


— 5) FSJ rsj                        (OAU     (AUCAI
                                                                                              -fc
                                                                       nimrnmrnrnmHiHiHimHinimmrnmrnmmrnmrn
                       zzrzrzzzz;
                                                 : zz zzz r z;
                                                                  z?II225I?i?IiIi55i
          immiri   szzzzZZZZmZmZmZZmrnmZmmmmmrnmrnrnrnrnrnmrnrnnirnrnrnrnrnrnrnrnrn

           -,aa   — — — — -•-•-i-i-.^ ~'o~'b"<~' — b — ~*bbbbbb-* — bbbbpbbbbbbbbbcsba
           3 § §                        <^>    S   5»     — 2 o   5;3-jS35Sooc»3c»-j3-^-.3Sa>u3^ia>a>taa>~.oD
TOTAL
ed FRUIT fi
PRODUC
nn INOESTIO
RISK
Lake
Walei
qpslm
Risk
Lake
Walpi
Deimal
Conlaci
Risk
InlanI
Bieasl milk TOT
Ingesllon CANC
RIS
TAL
CER
SK
-------
ABLE 2 Avq f. Mi(|li rn<) r.irif PI RM k'. f. tin
                                                i HCK Siili'.i'-.li.mr. f ,IM
                                           NONCARCINOGENIC HAZARD QUOTIENTS
Chemical
3.7.8 TCDO
.2.3.7.8 PeCDD
.2.3.4.7.8 HxCDD
.2.3.8.7.8 HxCDD
,2.3.7 8.9 HxCDD
.2,3.4.6,7,8-HpCDD
>CDD
,3.7.8-TCDF
,2.3.7.8 PeCDF
,3,4.7.8-PeCDF
2.3.4.7.8 HxCDF
.2.3.8,7.6 HxCDF
2,3.7,8.9 HxCDF
3487 8 HxCDF
2.3.4.6.7.8-HpCDF
2 3,4 7.8.9-HpCDF
CDF
Btiachloiobiphenyt
exaehkxoblphanyl
eptachkHobiptienyl
»nio(8)pyrana
9nio(b)fluofanlhona
s(2^rthy1h««Y()phlhal3le
arbon lotrachlorlda
ibar»z(a,h)anlhracene
(n)octy( phlhalale
sptachtof
§rachlofobeivena
9xachlorobutadian«
fxachlofocyclopanladien
iKachlofophena
dano(1,2.3-cd)pvreno
illmony
sank;
irlum
ityfllum
idmlum
iromlum (hexavalenl)
ad
»rcury
ckel
ilentum
VBI
allium
1C
>IOXIN TEQ
iRGANICS TOTAL (non
JORGANICS TOTAL
SUBAREA
Subaiea
E 1 hi emiss
E 1 hi emiss
E 1 hi 0miss
El hi emiss
E 1 hi emiss
E 1 hi amiss
El hi amiss
E 1 hi amiss
E 1 hi amiss
E 1 hi amiss
E 1 hi amiss
E \ hi amiss
E 1 hi amiss
E 1 hi amiss
El hi emiss
E 1 hi amiss
E1 hi emiss
E1 hi amiss
E 1 hi emiss
E 1 hi amiss
E 1 hi emiss
E 1 hi emiss
E 1 hi emiss
E 1 hi amiss
E 1 hi amiss
E 1 hi amiss
El hi amiss
E 1 hi amiss
E1 hi amiss
A E1 hi amiss
E 1 hi amiss
E1 hi emiss
E 1 hi amiss
El hi amiss
Ef hi amiss
». E 1 hi emiss
E1 hi amiss
E1 hi emiss
E1 hi amiss
E 1 hi amiss
El hi amiss
E1 hi amiss
El hi emiss
Et hi amiss
E t hi emiss
E 1 hi emiss
dioxmj E 1 hi emiss
E1 hi emiss
TOTAL El hi emiss
Soil
Inqeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 OE-09
25E 07
NT
42E 10
33E-10
40E4)7
22E06
20E 09
89E-07
NT
46E-08
24E 06
1 2E-08
38E-10
2 1E 08
99E-09
NT
2 7E 05
36E-09
2 7E 06
1 3E 08
4 7E-05
1 6E 09
NT
3 7E 06
79E 05
83E-05
Soil
Dermal
Contact
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E 10
29E W
NT
49E 11
396 11
4 7E-08
2 5E-07
24E 10
1 OE-07
NT
89E 10
4 6E 08
24E 10
73E 12
40E 10
1 9E-10
NT
5 3E 07
70E 11
52E 08
25E 10
9 IE 07
30E 11
NT
4 3E-07
1 5E 06
20E 06
Bnel
Inqeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
96E 04
1 7E-08
NT
1 5E 03
4 2E 07
1 9E 06
69E^>7
24E^)9
32E-03
NT
2 5E 07
59E^>6
7 7E-09
1 9E 10
1 IE 07
2 4E-08
NT
1 5E 05
36E 08
7 IE 06
26E 07
6 7E 04
26E 09
NT
57E 03
70E 04
64E 03
Poik
Inoeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
82E 05
BSE 09
NT
9 7E-05
30E 08
1 7E 06
79E 07
2 7E 09
20E 04
NT
1 OE 07
20E06
34E 08
1 6E-10
50E09
32E-08
NT
5 1E 05
1 6E 07
1 8E 04
5 7E 09
2 BE 03
6 7E-10
NT
36E 04
30E 03
3 4E 03
Chicken
Inqpsdon
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
22E 12
33E-11
NT
50E 12
84E-12
35E 09
1 7E 09
55E 12
32E-07
NT
84E-10
83E 07
14E 11
6 BE 12
22E-08
39E-10
NT
1 IE 05
27E 10
62E 06
75E 11
6 IE 04
64E 10
NT
33E 07
62E 04
63E 04
Olhci
Pmilliy
Inqoslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
35E 13
53E-12
NT
8 1E 13
10E 12
56E 10
2 7E 10
8 BE 13
5 2E-08
NT
1 4E-10
1 3E 07
23E 12
1 1E-12
3 6E 09
64E-11
NT
1 7E 06
44E 11
IDE 06
1 2E 11
9 BE 05
1 OE 10
NT
53E 08
1 OE 04
1 OE 04
Egg
Inqpstion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 OE-09
16E-08
NT
24E-09
3 1E-09
1 7E-06
79EX)7
26E-09
1 5E-04
NT
37E-09
4 IE 07
43E09
31E-12
20E-10
24E-10
NT
3 4E-07
1 7E 10
24E 06
5 7E 10
2 3E 04
25E-10
NT
1 6E 04
24E 04
39E 04
TOTAL
MEAT A
EGG
INGESTION
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 OE 03
4 OE 08
NT
1 6E 03
46E-07
53E06
23E06
7 BE -09
3 BE -03
NT
3 6E-07
92E06
4 6E 08
36E 10
1 4E 07
5 7E 08
NT
79E 05
20E 07
1 9E 04
2 7E07
4 4E 03
4 3E 09
NT
6 2E 03
4 7E 03
1 1E 02
Milk
Inqnslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
48E03
95E-08
NT
74E-03
2 1E 08
97E-06
35E-06
12E48
1 6E-02
NT
40E^17
2 BE 46
28E-07
2 7E-12
1 1E 07
1 OE-07
NT
3 1E 04
9 7E 08
1 7E 04
2 7E 05
54E 04
t IE 08
NT
28E 02
1 OE 03
2 9E 02
Chpose
Inqnstion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
. NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E-04
27E-09
NT
21E-04
5 9E 08
2 7E 07
9 9E 08
35E-10
4 5E-04
NT
1 IE-OS
7 BE 08
8 OE-09
76E 14
30E 09
29E 09
NT
8 BE 06
2 7E 09
4 7E 06
7 7E 07
1 5E 05
3 OF 10
NT
79E 04
29E 05
B ?E 04
Milk
Dessoils
Inqeshon
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 4E-04
47E-09
NT
3 re -04
1 OE-07
48E-07
1 BE -07
62E-10
80E-04
NT
2 OEM
1 4E-07
1 4E-08
1 3E-13
54E-09
52E-09
NT
16E 05
4 BE 09
84E 06
1 4E 06
2 7E 05
53F 10
NT
1 4E 03
52E 05
1 SF 01
Yogurt
Ingeslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 1E-04
22E-09
NT
1 7E-04
4 BE 08
22E-07
8 IE-OB
29E-10
37E-04
NT
92E-09
S4E-OB
65E-09
82E-14
25E^)9
24E-09
NT
72E06
2 2E 09
39E 06
63E 07
1 2E 05
2 5F 10
NT
65E 04
2 4F 05
6 7F 04
Cream
Inqnslion
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
NA
HA
flA
Butler
Inqeslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E 05
73E 10
NT
5 7E 05
1 6E 08
74E OB
2 7E 08
95E 11
1 2E 04
NT
3 IE 09
2 IE OS
2 2E 09
2 IE 14
83E 10
80F-10
NT
24E 08
75E 10
1 3E 06
2 1E 07
4 1E 06
87F 11
NT
2 2E 04
8 OF 06
2 ?f 04
  ume V App«ndi«V-17
-------
ABLE 2  Avg A Hi<|li r-n<1 r.,,,, ,., R...V, f. NH
                                       NONCARCINOOENIC HAZARD QUOTIENTS
Chemical
3.7.8 TCDD
2 3.7 8 PeCDD
.2.3 4.7.8-HnCDO
.2.3.8. 7.8 HxCDD
2,3.7.8.9 H«C DO
,2.3.4.6,7.8 HpCDO
COD
3.7.8-TCDF
2.3,7>PeCDF
,3.4.7.8 PeCOF
2.3.4. 7.8 HxCDF
2.3.8.7.8 HxCDF
2.3.7.8.9 HxCDF
3 4 6.7.8 HxCDF
2 3.4.6.7.8 HpCDF
2 3 4 7.8 9-HpCDF
CDF
Blrachlotoblphenyt
flxachloroblphenyl
nplachloioblpheny)
9nzo(a)pyiene
<*ruo(b)fluofanlhene
s(2-elhy1hexyl)phlhalate
aib- HI lelrachlorlde
iben* (a.h)anlht acene
i(n)octyl phlhalale
Bplachlor
axach' jfobanzene
axachlotobuladiene
9xachlarocyclopentadien<
niachlotophene
deno(1,2.3-cd)pytene
itimony
senlc
itlum
>ry1liiim
»dmlum
Homlum (hexavalenl)
ad
srcury
ckel
ilenium
Ivor
lallium
'1C
)IOXIN TEQ
)RGANICS TOTAL (non
TORGANICS TOTAL
SUBAREA
TOTAL
DAIRY
PRODUCT
Subaiea INGEST ION
HQ
Ethienuss NT
E 1 hi emiss NT
El hi emiss NT
Elhiemlss NT
E t hi emiss NT
E1 hi emiss NT
Elhiemlss NT
E 1 hi emiss NT
Elhiemlss NT
Elhiemlss NT
Elhiemlss NT
E 1 hi emiss NT
Elhiemlss NT
Elhiemlss NT
E 1 hi emiss NT
E1 hi emiss NT
E1 hi emiss NT
E1 hi emiss NT
E 1 hi emiss NT
El hi emiss NT
E 1 hi emiss NT
Elhiemlss NT
El hi emiss 5 3E 03
El hi emiss t OC-07
El hi emiss NT
E1 hi emiss 8 2E 03
El hi emiss 2 3E-06
El hi emiss 1 IE 05
E1 hi emiss 39E-06
e Et hi emiss ME 08
E1 hi emiss 1 8E-02
El hi emiss NT
Elhiemlss 4 4E-07
Et hi emiss 3 IE 06
Elhiemlss 3 1E-07
; Elhiemlss 30E-12
Elhiemlss 1 2E-07
Et hi emiss 1 2E-07
El hi emiss NT
E1 hi emiss 35E-04
El hi emiss 1 1E-07
E1 hi emiss 1 9E-04
El hi emiss 3 OE-05
E1 hi emiss 5 9E 04
E1 hi emiss 1 2E-08
Elhiemlss NT
-dio«m) E1 hi emiss 3 1E-02
El hi emiss 1 2E-03
TOTAL E1 hi emiss 3 2E-02
Exposed
Pioducfl
Inqpslion
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 7E-05
1 5E-05
NT
7 2E 06
t 3E-09
8 BE 08
76E-07
28E-10
1 1E-06
NT
1 7E-07
I2E-06
2 5E-08
46E-11
46E-07
1 3E-09
NT
4 BE -04
1' OE 08
2 IE 06
1 2E-07
30E 06
1 1E 07
NT
5 1E 05
49E-04
5 4E-04
Pinlprtpd
Ptoduce
Inqpslion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
89E 12
1 2E-05
NT
1 3E 12
1 IE 11
7 IE 08
64E-07
2 4E-10
59E-09
NT
87E-08
3 8E-07
1 IE -08
59E-12
2 3E-07
39E-IO
NT
40E 04
7 2E-09
1 3E 06
8 3E 08
1 2E 07
9 2E 08
NT
1 3E-05
40E-04
42E-04
I n;»fy
Piodurfl
Inqpstmn
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
58E 04
32E-06
NT
1 6E 04
2 BE 08
99E 08
1 9E-07
1 9E-10
6 3E-07
NT
1 9E-07
1 1E-06
3 5E-08
32E-11
32E-07
6 4E-10
NT
60E-04
2 7E 09
65E 07
96E 08
1 7E 06
4 1E 08
NT
7 IE 04
60E-04
1 IE 03
Root
Piorlur p
InqP'-IlOM
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E-11
35E-06
NT
3 3E-08
6 7E-10
4 OE 06
2 4E 06
66E-09
6 1E-06
NT
2 IE-ID
27E-10
1 9E-11
98E-16
8 1E-10
49E-I4
NT
1 5E-07
35E-13
3 7E-IO
20E-10
8 7E 12
2 7E 11
NT
1 6E-05
1 5E-07
1 6E-05
Fxpnlpd
f mil
liMjp^lion
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
MT
NT
NT
NT
NT
83E-05
35E-05
NT
1 7E 05
3 1E-09
2 1E 07
1 8E-06
6 7E 10
26E-06
NT
39E 07
2 BE 06
6 OE-08
1 1E-10
1 IE -06
3 1E 09
NT
1 1E 03
24E 08
49E 06
2 7E 07
7 IE 06
2 6E 07
NT
1 2E 04
1 2E-03
1 3E-03
Piolprlpd
Flint
Inqpslion t
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
6 1E 11
8 4E-OS
NT
9 1E-12
78E-11
4 BE 07
4 3E-08
1 6E-09
4 OE-08
NT
59E-07
26E-06
7 3E-08
40E 11
1 6E-06
2 6E-09
NT
2 7E 03
49EOB
89E 06
5 7E 07
8 2E 07
62E 07
NT
89E 05
2 7E-03
2 8E 03
TOTAL
FRUIT &
PRODUCE
NGEStlON
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
8 7E-04
1 5E4M
NT
1 8E 04
3 3E-08
50E-06
10E^)5
96E4I9
1 OE-05
NT
14E-06
80E06
20E-07
23E 10
36E-08
80E-09
NT
5 3E-03
93E 08
1 BE 05
1 IE 06
1 3E 05
1 IE 06
NT
1 OE 03
54E-03
64E-03
RIVPI
Wale.
Inqpstinn
HQ
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
24E 14
8 1E-12
NT
1 8E-15
1 4E-15
46E-12
t IE-It
87E-15
60E-12
NT
1 8E-12
52E-tt
45E-13
36E-15
1 4E 12
80E-14
NT
1 1E-09
93E-H
45E-11
5 1E-13
29E 10
6 IE 14
NT
30E 11
1 5E 09
1 5E 09
Riwt
Walni
Dpimnl
Contact
HO
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
74E-1t
76E-11
NT
1 9E-11
8 BE 13
30E^9
14E-09
27E-12
25E-08
NT
26E-13
7«E-12
65E-14
52E-t6
20E-13
1 2E-14
NT
1 6E-10
1 3E 14
64E 12
7 3E 14
4 1E II
88E 15
NT
29E 00
2 1E 10
IDF OB
Latin
Wain
Inqpslion
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MA
NA
MA
MA
HA
NA
(nkn
Walni
Drmnal
Contact
HQ
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
HA
HA
flA
NA
NA
TOTAL
HI
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
70E-03
1 5E 04
NT
1 OE 02
2 BE 06
2 IE 05
19E05
33EOB
2 1E-02
NT
23E-06
23E05
58E 07
98E-10
39E 06
1 
-------
ABl E 3  Avq S. Hnjli rnrl r.inroi Ri- k-, f. Hun. .in- fi HO'.


                                        NONCARCINOGENIC HAZARD QUOIIFNIS
                                          TOTAL                                                                     TOTAL                RIVOI                 Lake
                                          DAIRY    Eiposed   Prolprlpd    I pjfy      Rool     F'pospd   Piolprlert   FRUIT*     RIVPI      Wslpf      Lake      Water
                                        PRODUCT  Pioduce   Pinriuce    PioducB   Produce      Frurl       Fruil    PRODUCE   Walcr      Dermal     Wafer     Dormal
         Chemical            Suharea  INGESTIOU  Inqestinn   Inqesltnn    Uiqestn^n   Inqpslxui    Inqpiltnn   (nqcsltnn  INGESTION  Inpostion    Cnnlar.t   Inqesbon    Conlacl    TOTAL
                                            HO         HO        HO        HO        HO        HO        HO        HO        HO        HO        HQ       HO        t«



OTES
NA « Not applicable
MT » No torriclty inlormalron
HO * Hazard quotient
HI  • Ha/ard Indei
TEQ - TCDD equivalents
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ABLE 3  High End Avg Inhal-tion Risks and Nnncancn HQs m r.ubaipa F I
HEMICAL
ichlorodrfluoromethane
ichloroathane. 1.1- (Ethylidene dichlonde)
ichloroethane. 1.2-
ichloroethene. 1.1- (Vinyhdine chloride)
ichloroethene (trans). 1,2-
ichlorophenol. 2.4-
ichloropropane. 1.2- (Prrp/lene dichlonde)
Ichloropropene (els), 1.3-
ichloropropene (trans). 1 .3-
lethylphthalale
Imethoxytonzldin*. 3.3'-
Im«(hy1phenol, 2,4-
Imettiylphthalate
1 n butytphthalate
nrtio!olu«ne, 2,6-
lnfbo-2-methytphenol. 4.6
initrophenol. 2.4-
nrttoroluene. 2.4-
oxane. 1.4-
(n)octyt phthalate
2.4-
hyl methacrylale
hylbenzana
hylene dibfomlde
hylene oxide
hylene thlouraa
loranlhene
jorene
•rmaldehyde
irfural
iptachlor
•ptachlofoblphenyl
ixachlorobenzena
ixachloroblphenyt
ixachlorobutadlene
ixachlofocyclohexane gamma (Lindane)
ixachlorocyclopentadiene
ixachloroeihane
rxachlorophene »;
ixanone, 2-
leno( 1 .2,3-cd)pyrene
'phorone
ilelc hydrulde
ithoxychlof
ithyl | butyl ether
tthyl-2-Pentanone. 4- (MIBK)
'thylene chloride
ithylnaphthalene. 2-
inochloroblphenyt
phthalene
roanilme 2-
loanilme 3-
Inhalation
Slope
Factor
(mg/kg d)A 1
NA
NA
9 IE 02
1 2E»00
NA
NA
NA
1 3E 01
1 3E-01
NA
NA
NA
NA
NA
NA
NF
NA
NA
NA
NA
NA
NA
NA
7 6E-01
35E-01
NA
NA
NA
45E-02
NA
45E+00
NA
1 6E»00
NA
78E-02
NA
NA
1 4E-02
NA
NF
NA
NA
NA
NA
NA
NA
1 6E-O3
NF
NA
NA
NA
NF
RAC
005
0 125
NA
0007875
00175
0 002625
0001
0005
0005
07
NA
00175
NA
00875
0000875
NF
000175
000175
NA
00175
000875
007875
025
000005
NA
000007
0035
0035
0 175
00125
0000438
NA
00007
NA
0000175
0000263
0000018
0000875
0000263
NF
NA
0 175
04375
0004375
0 75
002
0 75
NF
NA
0035
000005
NF
Inhalation
RfD
(mg/kg d)
1 4E 02
3 BE 02
NA
23E 03
50E 03
75E 04
29E 04
1 4E 03
1 4E 03
20E 01
NA
50E-03
NA
25E 02
25E04
NF
50E 04
5 OE -04
NA
50E 03
25E 03
23E 02
7 IE 02
1 4E 05
NA
20E 05
1 OE 02
1 OE 02
50E 02
36E 03
1 3E 04
NA
20E-04
NA
50E 05
75E 05
50E 06
25E 04
75E-05
NF
NA
50E 02
1 3E 01
1 3E 03
2 1E-01
5 7E 03
2 IE 01
NF
NA
1 OE 02
1 4E 05
fJF
High end
Emission
Rale
(gKec)
49E 04
2 5E 05
25E 05
25E 05
25E 05
1 IE 05
25E 05
2 5E 05
25E 05
36E 05
1 2E 04
1 IE 05
1 IE 05
20E OS
1 IE 05
1 IE 05
t 1E 05
1 IE 05
49E 04
1 IE 05
39E 05
4 9E 04
75E 04
1 2E 04
3 1E 05
1 5E-10
1 IE OS
6 7E 06
6 IE 04
1 1E-05
1 1E 06
28E 08
1 IE-OS
2 BE 08
1 OE 04
55E-05
1 IE 05
1 IE 05
J2E 05
64E 05
1 IE 05
67E 06
1 2E 04
1 IE 06
25E 05
25E 05
62E 04
42E 05
30E 08
t 1E 05
6 7E 06
6 7E 06
Subarea
E1 avg
El avg
El avg
E 1 avg
El avg
E 1 avg
El avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
Et avg
E1 avg
Et avg
E1 avg
El avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
Et avg
El avg
El avg
E1 avg
Et avg
El avg
El avg
E1 avg
E1 avg
El avg
El avg
El avg
E1 avg
El avg
El avg
El avg
El avg
El avg
El avg
E1 avg
E 1 avg
E 1 avg
Adult
Cancer
Risk
NT
NT
7 7E 11
t OE 09
NT
NT
NT
1 IE 10
1 1E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
30E-09
36E 10
NT
NT
NT
93E-10
NT
1 7E-10
NT
60E-10
NT
2 7E-10
NT
NT
52E-12
NT
NT
NT
NT
NT
NT
NT
NT
35E-11
NT
NT
NT
NT
NT
Child
Cancer
Risk
tn
NT
58E 11
76E 10
NT
NT
NT
82E 11
82E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
2 2E-09
27E-10
NT
NT
NT
69E-10
NT
1 3E-10
NT
45E-10
NT
20E-10
NT
NT
39E-12
NT
NT
NT
NT
NT
NT
NT
NT
26F 11
NT
NT
NT
NT
NT
School age
Cancer
Risk
NT
NT
35E 11
46E 10
NT
NT
NT
50E 11
50E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E-09
1 6E-10
NT
NT
NT
42E-10
NT
76E-11
NT
27E-10
NT
1 2E-10
NT
NT
24E-12
NT
NT
NT
NT
NT
NT
NT
NT
1 6E-11
NT
rn
NT
NT
NT
Farmer
Cancor
Risk
NT
NT
1 OE 10
1 4E 09
NT
NT
NT
1 5E 10
1 5E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
40E 09
48E-10
NT
NT
NT
1 2E-09
NT
22E-10
NT
80E-10
NT
36E-10
NT
NT
70E-12
NT
NT
NT
NT
NT
NT
rn
rn
46E 11
rn
rn
rn
rn
rn
                                                                                                                                             Adult     Child   School age   T armor
                                                                                                                                           Noncancer Noncancet Noncancer Noncancer
                                                                                                                                              HQ       HO       HO       HQ
2 7E 06
56E 08
NT
88E 07
40E07
1 2E 06
69E 06
1 4E 06
t 4E-06
1 4E 08
NT
1 7E-07
NT
6 5E 08
35E06
NT
7E06
7E 06
NT
7E07
2E06
7E06
84E07
64E 04
NT
58E-10
8 7E 08
5 3E-08
9 6E 07
2 4E^)7
70E07
NT
44E-06
NT
1 6E 04
58E-05
1 7E^)4
35E06
3 4E-05
NT
NT
1 IE 08
7 3E 08
70E-08
93E 09
35E 07
2 3E 07
NT
NT
8 7E 08
3 7F 05
rn
1 OE 05
2 IE 07
NT
33E-06
1 5E 06
44E06
26E-05
52E06
52E06
53E^>8
NT
65E-07
NT
2 4E 07
1 3E^B
NT
65E^)6
65E-06
NT
65E^)7
46E46
65E-06
3 IE 06
24E-03
NT
22E09
33E-07
20E^)7
36E06
91E-07
26E-06
NT
16E-05
NT
60E 04
2 2E 04
65E4M
1 3E 05
1 3E^)4
NT
NT
40E 08
2 7E 07
26E07
35E 08
1 3E OG
eer 07
rn
rn
3 3E 07
1 -If 04
rn
62E 06
1 3E 07
NT
20E 06
90E07
26E 06
16E05
3 IE 06
3 1E 06
3 2E-08
NT
39E-07
NT
1 5E-07
79E 06
NT
39E06
39E-06
NT
39E 07
2 BE 06
39E 06
1 9E 06
1 4E-03
NT
1 3E 09
20E 07
1 2E 07
22E06
55E 07
t 6E-06
NT
99E-06
NT
36E 04
1 3E 04
39E 04
79E 06
7 7E-05
NT
NT
2 4E 08
1 6E 07
1nE 07
2 IE 08
7 BE 07
57F.-07
NT
NT
20E 07
fl 4F 05
rn
27E06
56E 08
NT
88E 07
40E07
1 2E 06
69E 06
1 4E 06
1 4E 06
1 4E 08
NT
1 7E-07
NT
65E 08
35E-06
NT
7E06
7E-06
NT
7E 07
2E06
7E^)6
84E07
64E 04
NT
58E 10
8 7E 08
53E 08
96E07
24E07
70E 07
NT
44E-06
NT
1 6E 04
5 BE 05
1 7E 04
35E 06
34E 05
NT
NT
1 IE 08
73E 08
70E 08
93E 09
35E 07
2 IF 07
NT
NT
8 7E 08
3 7F. 05
rn
 ume V Appendix V 1 7
-------
ABLE 3  High End Avg ,.  jlnlion Ri<,k<; and flnncancoi IIU', m
                                                                F 1
.HEMICAL
litroamline, 4-
Irtrobflnzflna
litrophenol, 2-
Irtropnenol, 4-
1 Nrtroso di n butytamme
1 NitTOSo-di-n-pfopytamme
1 Nrtjosodlphenylamine (Diphenytamlne)
lonachlofobiphenyl
Ictachlotobtphenyt
entachlofob«nrene
'«ntachloroblph«ny1
•nt»chlofonHrob»nz»n*
entachlorophenol
henanthren*
henot
yrene
ahote (5-(2-Propenyl)-1,3 benzodioxole)
tyi»n«
etrachlofoblphenyl
etrachlofoethane. 1,1 1 2
•bachloroethan*, 1.1,2,2-
elrac hloromh* n«
ebachlwophenol 2 3.4,6
oluene
iichlofo-1,2.2-trtfluofo«thane. 1.1.2-
ilchlorotxnzene, 1,2.4-
rlchloroblphenyl
rlchlofo«ttiane, 1.1.1- (Methyl chloroform)
rlchloro«thaina, 1.1.2-
tichlorotthvn*
rlchlorotluofom ethane
rtchlorophtnol. 2,4.5-
rrcnlofoph«nol, 2.4.6-
inyl •cetat*
Inyt chloride
ytene. m/p- (m/p-Dlmettiyt benzene)
ylena. o- (o-Dtmethyt benzene)
,3.7.8-TCDO
,2.3.7.ePCDD
234 7.8-HxCDO
2,3.8.7.8-HxCDO
2.3.7,8.9-HxCDD
2.3,4.8. 7,8-HpCDD
iCDD
3.7.8-TCDF
23.7.8-PCDF
3.4,78-PCDF
2 3 4. 7.8 HxC OF
2 36,7,8-HxCDF
346.7,8 HxC DF
Inhalation
Slope
Factor
mg/kg d)' 1
NF
NA
NF
NF
54E*00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
2 OE-01
20E-03
NA
NA
NA
NA
NA
NA
5 7E 02
60E-03
NA
NA
1 OE 02
NA
3 OE-01
NA
NA
1 5E»05
75E»04
5E*04
5E»04
5E»04
5E«03
5E*02
5E»04
5E+03
5E+04
5E«04
5E«04
5E+04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02625
NA
0525
0 02625
NF
025
NA
002625
NA
000875
002625
0 t
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg d)
NF
t 4E 04
tIF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E 01
7 5E-03
NF
7 IE 02
NA
75E 03
NA
25E 03
/5E 03
29E 02
2 1E»00
1 4E 02
NA
7 1E 02
1 OE 03
NA
50E 02
2 5E 02
NA
1 4E-02
NA
50E 01
5 OE-01
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
High pnd
Emission
Rale
(g/sec)
6 7E 06
t IE 05
6 7E 06
1 IE 05
1 2E 04
6 7E 06
6 7E 06
2 BE 08
2 BE 08
4 BE 05
2 BE 08
34E 05
1 IE 05
6 7E 06
1 1E 05
1 IE 05
1 2E 04
40E 05
2 BE 08
1 1E 05
1 1E 05
80E 05
6 BE 06
1 OE 03
33E 04
1 1E 05
5 BE 08
25E05
25E-05
3 1E 05
4 9E 04
1 IE 05
1 1E-05
64E 05
4 9E 04
56E-04
1 1E 05
22E-11
9SE 11
1 2E-10
22E 10
1 5E-10
1 7E 09
98E 09
1 1E 10
43E 10
60E 10
1 9E 09
t 7E 09
20E 09
Subaroa
E 1 avg
El avg
E 1 avg
El avg
El avg
E 1 avg
El avg
El avg
E1 avg
El avp
El avg
E1 avg
El avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
El avg
E1 avg
E1 avg
Et avg
El avg
E1 avg
El avg
E1 avg
E1 avg
El avg
El avg
E1 avg
El avg
El avg
E1 avg
El avg
Et avg
El avg
El avg
E1 avg
El avg
El avg
El avg
El avg
E1 avg
E1 avg
El avg
E1 avg
El avg
El avg
E t avg
El avg
Oft silp
V.ipoi
Cone
(llg/m3)
t 9E 06
3 2E 06
1 9E 06
32E 06
35E 05
1 9E 06
1 9E 06
8 IE 09
8 IE 09
1 4E 05
8 IE 09
9 BE 06
32E 06
1 9E 06
32E 06
32E 06
33E 05
1 2E 05
8 IE 09
32E 06
32E 06
23E 05
20E-06
30E 04
96E 05
32EO6
1 7E-08
7 3E 06
73E-06
90E 06
1 4E 04
32E 06
32E-06
1 9E 05
1 4E-04
1 6E04
32E06
63E-12
2 7E 11
36E-11
63E 11
45E 11
49E 10
2 8E-09
33E 11
1 3E-10
1 BE 10
54E-10
50E 10
57E 10
Cancer
Adult
DOSP
(mg/kg d)
2 3E 10
3 7E 10
2 3E 10
3 ?E 10
4 1E 09
23E 10
23E 10
95E 13
95E-13
1 6E -09
95E 13
1 IE 09
3 7E 10
23E 10
3 7E-10
3 7E 10
39E 09
1 4E 09
95E-13
37E-10
37E 10
27E09
23E 10
35E-08
1 1E-08
3 7E-10
20E-12
85E-10
85E-10
1 1E-09
1 7E-08
37E-10
37E-10
22E-09
1 7E-08
1 9E-08
37E-10
74E 18
32E 15
43E 15
74E-15
53E-15
57E 14
33E 13
39E 15
1 5E 14
2 IE 14
63E 14
58E 14
6 7E 14
Cancer
Child
Done
(mg/kg d)
1 7E 10
?8E 10
1 7E 10
28E 10
3 1E 09
1 7E 10
1 7E 10
7 IE 13
7 IE 13
1 2E 09
7 1E-13
86E-10
2 BE 10
1 7E-10
28E-10
2 BE 10
2 9E 09
1 OE 09
7 1E-13
28E-10
28E 10
20E09
1 7E-10
2 6E 08
84E-09
28E-10
1 5E-12
64E-10
64E-10
79E-10
1 2E-08
28E-10
28E-10
16E09
1 2E 08
1 4E-08
2 8E-10
55E-16
24E-15
32E 15
55E-15
39E-15
43E 14
25E 13
29E 15
1 1E 14
1 5E 14
4 7E 14
43E 14
50E-14
Cancer
School ago
Dose
(mg/kg d)
1 OE 10
t 7E 10
1 OE 10
t 7E 10
1 9E 09
1 OE 10
1 OE-10
43E 13
43E 13
73E 10
43E 13
52E 10
1 7E-10
1 OE-10
1 7E-10
1 7E-10
1 BE 09
62E 10
43E-13
1 7E-10
1 7E-10
1 2E 09
1 OE-10
1 6E-08
51E-09
1 7E-10
89E-13
38E-10
38E-10
48E-10
75E-09
1 7E-10
1 7E-10
99E-10
75E-09
87E-09
1 7E-10
33E 18
15E 15
1 9E 15
33E 15
24E 15
26E 14
1 5E 13
1 8E-15
67E 15
93E 15
2 BE 14
26E 14
30E 14
Cancer
F armer
Dose
(mg/kg d)
30E 10
50E 10
30E 10
50E 10
55E-09
30E 10
30E 10
1 3E 12
1 3E 12
22E 09
1 3E 12
1 5E 09
50E 10
30E-10
50E 10
50E-10
52E 09
1 8E 09
1 3E-12
50E 10
50E 10
36E-09
3 1E-10
4 7E 08
1 5E-08
5 OE-10
26E 12
1 1E^»
1 IE 09
1 4E-09
22E 08
5 OE-10
5 OE-10
29E-09
22E4W
26E-08
50E-10
98E 16
43E-15
57E-15
99E-15
70E 15
7 7E-14
44E 13
52E 15
20E 14
2 7E 14
84E 14
7 BE 14
B9F 14
Noncancer
Adult
Dose
(mg/kg-d)
53E-10
87E 10
53E 10
8 7E 10
96E09
53E 10
53E 10
22E 12
22E 12
38E 09
22E 12
27E-09
87E-10
53E-10
87E 10
87E 10
9 IE 09
32E 09
22E 12
87E 10
87E-10
64E-09
54E 10
8 2E 08
26E-08
87E-10
46E-12
20E-09
20E09
25E-09
39E-08
8 7E-10
8 7E-10
51E-09
39E 08
45E-08
8 7E-10
1 7E-15
75E 15
99E 15
1 7E 14
12E 14
1 3E 13
7 BE 13
9 IE 15
35E 14
4 BE 14
1 5E 13
1 4E 13
1 6C 13
^oncancei
Child !
Dose
(mg/kg d)
20E 09
33E 09
20E 09
33E09
36E 08
20E 09
20E09
83E 12
83E 12
1 4E-08
83E 12
1 OE 08
33E-09
20E09
33E09
33E09
34E 08
1 2E 08
83E-12
33E09
3 3E^)9
24E08
2 OE-09
3 1E 07
98E08
33E09
1 7E 11
74E49
74E09
92E09
1 5E-07
33E 09
33E09
1 9E-08
1 5E 07
1 7E 07
33E-09
64E-15
28E 14
3 7E 14
85E 14
46E 14
50E 13
29E 12
34F 14
1 3F. 13
t BE 13
5r)E 13
5 IF 13
SRf 13
Noncancer
School age
Dose
(mg/Kg d)
1 2E 09
20E 09
1 2E 09
20E 09
2 2E 08
1 2E 09
1 2E 09
50E 12
50E 12
85E-O9
50E 12
60E09
20E09
1 2E-09
2 OE-09
20E4)9
2 1E4>8
73E09
50E 12
2 OE-09
2 OE-09
t 4EXW
1 2E^)9
1 BE 07
59E-08
20EO9
1 OE 11
4 5E-09
45EO9
55E 09
8 BE 08
20E 09
20E09
1 2E 08
8 BE 08
1 OE 07
2 OE-09
39E 15
1 7E 14
22E 14
39E 14
28E 14
30E 13
1 BE 12
2 IE 14
78E 14
1 IE 13
33E 13
3 1E 13
35F 13
•loncancer
Farmer
Dose
(mg/kg d)
53E 10
87E 10
53E 10
B7E-10
96E 09
53E 10
53E 10
22E 12
22E 12
3 BE 09
22E 12
27E09
87E 10
53E 10
87E 10
87E 10
9 IE 09
3 2E 09
22E 12
8 7E 10
87E 10
64E 09
54E 10
82E 08
26E08
8 7E 10
46E 12
20E09
20E09
25E09
39EO8
87E 10
8 7E-10
5 1E-09
39E-08
45E08
8 7E-IO
1 7E 15
75E 15
99E 15
1 7E 14
1 2E 14
1 3E 13
7 8E 13
9 IE 15
35E 14
48E 14
1 5E 13
' 1 -IF 13
1 6F 13
 alume V. App«ndi« V-17
-------
VBt E 3  High End Avg Inhalation F?ir,l"; nnd Nonc.incci HOs in r.tib.irp.i F 1
MEMICAL
Itoaniline. 4-
trobenzena
trophenol, 2-
trophenol, 4
Nttroso-dl-n-butylamine
Nitrovwli-n-ptopylamine
Nrbosodlphenylamln* (Diphenylamine)
inachloroblphenyl
rtochlofoblphenyl
intachlOfotMnzen*
mtachlofoblphenyt
mtachlofonttrobenzene
intachlorophenol
lenanthrene
lenol
rene
itrole (5-(2-Prop«nyl} 1 .3-ben*odioxole)
fttnt
Irachloroblphenyl
trachlotoethane 1,1,1 2-
bachlofoethane. 1.1.2.2-
trachloroethene
Irachlorophenol, 2.3.4,6-
luene
chtoio-1.2.2 blfluoio«ttitn». 1,1.2
chk>rob«nzen«, 1,2,4-
chloroblphenyl
chloroethane, 1,1,1- (Methyl chloroform)
chloroethane. 1,1,2-
ehlofoethene
chkxofluorofnethane
chloiophenol. 2,4,5-
chlofophvnol. 2,4,6-
lyt acetate
iy1 chloride
ene, m/p- (m/p Dimethyl benzene)
en*, o- (o-D(mettiy1 benzene)
7.8-TCDO
3.7.8-PCDD
34,7,8-HxCDO
36 78-HxCDO
3 78.9HxCDO
,3.46,7.8-HpCOO
OD
78TCDF
3.78-PCDF
4 7 8 PCDF
i 34 7 8 HxCDF
367 8 HxCDF
4 6,7 8 HxCDF
nhalation
Slope
Factor
(mg/kg-d)"-!
NF
NA
NF
NF
54E+00
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NF
NA
NA
26E 02
2 OE-01
2 OE-03
NA
NA
NA
NA
NA
NA
57E-02
6 OE-03
NA
NA
1 OE-02
NA
3 OE-01
NA
NA
1 5E+05
7 5E+04
5E+04
5E+04
5E«04
5E»03
5E*02
5E+04
5E+03
5E+04
5E«04
5E»04
5E»04
RAC
(mg/m3)
NF
00005
NF
NF
NA
NA
NA
NA
NA
NA
NA
0 002625
0 02825
NA
0525
0 02625
NF
025
NA
002625
NA
000875
002625
0 1
75
005
NA
025
00035
NA
0 175
00875
NA
005
NA
1 75
1 75
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Inhalation
RfD
(mg/kg d)
NF
1 4E 04
NF
NF
NA
NA
NA
NA
NA
NA
NA
75E-04
75E-03
NA
1 5E-01
75E-03
NF
7 IE 02
NA
75E 03
NA
25E 03
75E 03
29E-02
2 1E«00
1 4E-02
NA
7 IE 02
1 OE-03
NA
50E 02
2 5E-02
NA
1 4E-02
NA
50E01
5 OE-01
NA
HA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
High end
E mission
Rate
6 7E 06
1 IE 05
6 7E 06
1 1E 05
1 2E 04
6 7E 06
6 7E 06
2 BE 08
2 BE 08
4 BE 05
2 BE 08
34E05
1 1E4>5
67E06
1 IE-OS
1 1E 05
1 2E 04
40E 05
2 8E 08
1 IE 05
1 IE 05
80E05
68E 06
1 OE 03
33E04
1 1E 05
5 BE 08
25E05
25E 05
3 IE 05
49E 04
1 IE 05
1 IE 05
64E05
49E04
56E 04
1 IE 05
22E It
95E 11
1 2E 10
22E 10
1 5E 10
1 7E 09
98E 09
1 IE 10
4 3E 10
60E 10
1 9E 09
1 7E 09
20E 09
Subarea
El avg
El avg
El avg
El avg
E1 avg
El avg
Et avg
El avg
E1avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
El avg
Et avg
El avg
El avg
El avg
E1 avg
El avg
El avg
E1 avg
Et avg
Et avg
Et avg
E1 avg
El avg
E1 avg
El avg
E1 avg
Et avg
El avg
Et avg
El avg
El avg
El avg
El avg
El avg
E1 avg
E1 avg
El avg
El avg
El avg
Et avg
El avg
Et avg
E1 avg
Adult
Cancer
Risk
NT
NT
NT
NT
22E 08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
97E-12
76E-11
55E-12
NT
NT
NT
NT
NT
NT
49E 11
63E-12
NT
NT
37E-12
NT
50E-09
NT
NT
1 1E-10
24E 10
64E 11
1 IE-10
79E 11
86E 11
50E 11
59E 11
1 1E-10
1 5E 09
95E-10
8 7E 10
1 OE 09
Child
Cancer
Risk
NT
NT
NT
NT
1 7E-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
72E-12
57E-11
4 IE-12
NT
NT
NT
NT
NT
NT
36E-11
4 7E-12
NT
NT
2BE-12
NT
37E-09
NT
NT
B2E 11
1 BE 10
48E 11
83E 11
59E 11
64E 11
3 7E 11
44E 11
83E It
1 2E-09
7 IE 10
65E 10
75E-10
School age
Cancer
Risk
NT
NT
NT
NT
1 OE-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
44E-12
34E-11
25E-12
NT
NT
NT
NT
NT
NT
22E-11
28E-12
NT
NT
1 7E-12
NT
23E-09
NT
NT
50E-11
1 IE 10
29E 11
50E It
36E 11
39E 11
23E 11
26E-11
50E 11
70E 10
43E-10
39E-10
45E-10
Farmer
Cancer
Risk
NT
NT
NT
NT
3 OE-08
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E-11
10E-10
74E-12
NT
NT
NT
NT
NT
NT
65E11
83E-12
NT
NT
50E-12
NT
67E-09
NT
NT
1 5E-10
32E-10
BSE 11
1 5E-10
1 1E 10
1 IE 10
6 7E 11
7 BE 11
1 5E 10
2 IE 09
1 3E 09
1 2E 09
1 3E 09
                                                                                                                                                     Adult      Child   School age  Farmer
                                                                                                                                                  Noncancer Noncancer Noncancer Noncancer
                                                                                                                                                      HQ        HQ        HQ        HQ
NT
6 IE 06
NT
- NT
NT
NT
NT
NT
NT
NT
NT
36E-06
1 2E-07
NT
5 BE -09
1 2E-07
NT
45E-08
NT
1 2E-07
NT
25EO6
7 2E-08
29E4)6
1 2E-08
6 IE-OB
NT
2 BE 4)8
20EX»
NT
78E-07
35E-08
NT
36E-07
NT
90E-06
1 7E-09
NT
NT
NT
NT
NT
NT
NT
m
NT
NT
NT
NT
NT
NT
2 3E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 3E-05
44E-07
NT
2 2E 08
44E-07
NT
1 7E-07
NT
44E-07
NT
95E-06
27E-07
1 IE-OS
46E48
2.X-07
NT
10EO7
74E-06
NT
29E06
13E-07
NT
13E-06
NT
33E07
65E-09
NT
NT
NT
NT
NT
NT
NT
NT
NT
in
NT
NT
in
NT
1 4E-05
NT
NT
NT
NT
NT
NT
NT
NT
NT
8 IE-OS
26E4)7
NT
13E-08
26E-07
NT
1UE-07
NT
26E-07
NT
5 BE 06
16E4J7
65E06
2 BE 08
1 4E-07
NT
63E08
45E-08
NT
18E 06
79E4W
NT
B 1E-07
NT
20E 07
39E-09
NT
NT
NT
NT
NT
NT
NT
NT
IIT
NT
NT
fIT
fIT
NT
61E-06
NT
NT
NT
NT
NT
NT
NT
NT
NT
36E 06
12E07
NT
5 BE 09
1 2E-07
NT
45E-08
NT
12E-07
NT
25E 06
72E08
29E06
12E-06
6 1E-08
NT
28E08
20E4W
NT
7 BE 07
35E4)8
NT
36E-07
NT
90E-OB
1 7E 09
NT
NT
NT
NT
NT
NT
NT
NT
III
NT
NT
NT
NT
  im» V Appendix V 1 7
-------
ABLE 3  High End Av
                        Mion Risks and Noncancer HQ*» in Subarra F 1
;HEMICAI_
i.2.3.7.8.9HxCOF
.2.3 4.6,7.8 HpCDF
,2.3,4,7,8,9 HpCDF
>CDF
Dioxln TEQ
\lumlnum
uittmony
iraenlc
larlum
ton/Ilium
;admlum
:hromlum (h*xaval«nt)
:hromlum (trtvalant)
~.opp«t
•ad
1»icury (and MsHg)
llckel
•lenlum
ilv«(
halllum
Inc
lydrogen chlorida
ot»< nltrogan oxides (NOx)
otat sulfur oxides (SOx)
'articulate matter
tesplrable participates
Inhalation
Slope
Factor
(mg/kg-d)A-1
1 5E»04
t 5E«03
1 5E«03
1 5E»02

NA
NA
50
NA
84
81
41
NA
NA
NA
NA
084
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA

NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00175
0004375
0004375
0000061
02625
000175
NA
NA
NA
NF
Inhalation
RID
(mg/kg d)
NA
NA
NA
NA

NA
10E 04
75E 05
36E 05
1 3E-03
1 3E 04
1 3E 03
25E-01
NA
NA
2 1E05
50E 03
1 3E^)3
t 3E-03
1 BE -05
7 5E-02
50E-04
NA
NA
NA
NF
High end
Emission
Rate
8
5 1E-10
1 2E-09
4 1E-09
1 1E-06
82E-05
3 1E-08
25E-06
25E-08
Cancel
Child
Dose
(mg^kg d)
9 BE 15
3 3E 13
46E 14
92E 13
1 BE 12
6 IE 09
1 IE 10
94E 10
3 8E 09
84E 13
4 IE 10
1 8E-11
1 8E 11
24E-09
1 IE 09
36E-08
1 3E-10
1 2E-08
38E-10
86E-10
31E-09
81E-07
62E-05
23E^W
1 BE-06
1 8E-06
Cancer
School age
Dose
(mg/kg d)
59E 15
20E 13
2 BE 14
56E 13
1 1E-12
37E-09
65E 11
57E-IO
23E 09
51E 13
25E-10
1 1E-11
1 1E-11
1 4E-09
66E-10
22E*8
77E-11
72E-09
23E-10
52E-10
1 BE -09
49E^)7
37E-05
1 4E-06
1 1E^>6
1 1E-06
Cancer
Farmer
Dose
(mg/kg d)
1 7E 14
59E 13
82E 14
1 6E-12
32E-12
1 IE-OS
19E-10
1 7E-09
68E-09
1 5E-12
73E 10
32E-11
32E-11
43E-09
20E-09
64E-08
2 3E-10
2 1E-00
68E-10
1 5E-09
54E-09
1 5E-OS
1 1E-04
4 1E-06
33E^)6
33E-06
Noncancer
Adult
Dose
(mg/kg d)
3 IE 14
1 OE 12
1 4E 13
29E 12
56E-12
19E^8
33E 10
29E-09
12E^8
26E-12
t 3E-09
56E-11
56E 11
75E-09
34E-09
1 1E^)7
4 OE-10
37E-08
1 2E-09
27E-09
95E-09
25E4»
19EXM
72E-08
57E^6
57E-08
Noncancer
Child
Dose
(mg/kg d)
1 1E-13
38E 12
53E 13
1 IE 11
2 1E-11
7 IE 08
1 2E-09
1 IE-OB
45E-OB
9BE-12
47E-09
2 1E-10
21E-10
2 BE 08
1 3E-08
42E07
1 5E 09
1 4E-07
45E09
10E08
36E 08
95E06
7 2E 04
27E-05
21E05
2 1E-05
Noncancer
School-age
Dos«
(mg/kg d)
69E-14
23E 12
32E 13
65E 12
1 3E-11
4 3E 08
75E-10
6 BE 09
27E-08
59E-12
29E-09
1 3E-10
1 3E-10
1 7E-08
77E-09
25E-07
9 OE-10
84E08
27E09
61E-09
2 2E 08
57E06
4 3E 04
1 6E 05
1 3E 05
1 3E-05
Noncancei
Farmer
Dose
(mg/kg d)
3 IE 14
10E 12
14E 13
29E 12
56E 12
19E08
33E-10
29E09
1 2E 08
26E 12
1 3E^9
56E 11
56E 11
75E09
34E 09
1 IE 07
40E 10
37E08
1 2E09
27E09
95E^)9
25E06
1 9E 04
72E 06
57E 08
5 7E4)8
 IOTES:
  NA-Notapp)lcabl»
  NF-Not found        x
  NT • No texlctty Informattdn
  HO - Huard quotient
  HI  -Hazard Index
 Dlume V, Appendix V 17
-------
ABLE 3  High End Avg Inhalation Risks and Noncancci HQs in Subaipa F 1
:HEMICAL
2 3.7,8.9 HxCDF
7.3.4 8.7.8 HpCDF
2.3.4.7,8.9-HpCDF
>CDF
Dioxln TEQ

lumlnum
ntjmony
rsente
ailum
nryllium
admlum
hromlum (hexavalent)
hrorr.lum (Wv«len!|
opper
»ad
etcury (and MeHg)
ickel
stenlum
tver
lalllum
i 1C
rdrogen chloride
i tal nitrogen oxides (NOx)
i 'tal sulfuf OKktes (SOx)
; iiDculat* matt»(
; reptnibto particulaHn
Inhalation
Slope
Factor
(mg/Vg-d)A-
1 5E*04
1 5E+03
I 5E + 03
1 5E»02


NA
NA
50
NA
84
61
41
NA
NA
NA
NA
004
NA
NA
NA
NA
NA
NA
NA
NA
NF
RAC
(mg/m3)
NA
NA
NA
NA


NA
000035
0000263
0000125
0004375
0000438
0004375
0875
NA
NA
0000075
00)75
0004375
0004375
OOO0061
02825
000175
NA
NA
NA
NF
Inhalation
RfD
(mg/kg d)
NA
NA
NA
NA


NA
1 OE 04
75E-05
36E05
1 3E-Q3
1 3E 04
1 3E 03
25E-01
NA
NA
2 IE 05
50E 03
1 3E 03
1 3E-03
1 BE 05
7 5E-02
50E-04
NA
NA
NA
NF
High end
Emission
Rale
(g/sec)
39E 10
1 3E 08
1 8E 09
36E 08
701E 08

24E4M
42E 06
37E 05
15E-04
33E-08
1 6E 05
7 1E-07
7 IE 07
94E^K
43E 05
1 4E 03
50E 06
4 7E 04
1 5E OS
34E^)5
1 2E^4
32E 02
24E«00
9 IE 02
7 2E 02
7 2E-02
Subarea
El avg
El avg
Et avg
El avg


El avg
Et avg
El avg
E1 avg
E1 avg
Et avg
E1 avg
E1 avg
El avg
El avg
E1 avg
El avg
E1 avg
Et avg
E1 avg
El avg
El avg
El avg
61 avg
El avg
El avg
T_»_I r»i_L
Adult
Cancer
Risk
20E 10
66E 10
92E 11
1 BE 10
6 IE 09

NT
NT
83E-08
NT
94E 12
33E09
99E 10
NT
NT
NT
NT
14E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
4 **- flf
Child
Cancer
Risk
1 5E 10
49E 10
69E 11
1 4E 10
4 BE -09
t
NT
NT
4 7E-08
NT
7 IE 12
25E09
7 4E-10
NT
NT
NT
NT
1 1E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
* Mf AA
3chool-age
Cancer
Risk
89E 11
30E 10
4 1E-11
83E 11
29E 09

NT
NT
2 8E-08
NT
43E-12
1 5E-09
45E-10
NT
NT
NT
NT
65E-11
NT
NT
NT
NT
NT
NT
NT
NT
NT
e 4P n«
Farmer
Cancer
Risk
26E-10
88E 10
1 2E 10
25E-10
85E*9

NT
NT
84E-08
NT
1 3E-11
44E-09
13E-09
NT
NT
NT
NT
1 9E-10
NT
NT
NT
NT
NT
NT
NT
NT
NT
« ff nt
 )TES:
 MA • Not appllceble
 MF- Not found
 v»T • No toxtetty lnforroa«6h
  )Q • Haiard quotient
 -II -Hazard Index
                                                                                                                                             Adult      Child   School-age  Farmer
                                                                                                                                           Noncancer Noncancer Noncancer Noncancer
                                                                                                                                              HQ        HO        HQ        HQ
NT
NT
NT
NT
NT
NT
33E-06
39E-05
3 3E-04
2 1E-09
1 OE-05
4 5E 08
2 3E-10
NT
NT
5 2E-03
7 9E 08
30E4»
95E-07
1 5E-04
1 3E-07
51E-03
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
1 2E-05
15E-04
1 2E-03
78E-09
38E-05
1 7E-07
84E-10
NT
NT
1 9E 02
30E4)7
1 1E 04
36E-06
58E-04
47E-07
19E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
75E-06
88E05
75E04
47E^)9
23E^5
10E-07
51E-10
NT
NT
1 2E-02
18E-07
67E4)5
22E^8
35E4M
29E-07
1 1E-02
NT
NT
NT
NT
NT
NT
NT
NT
NT
NT
33E-06
39E05
3 3E 04
2 1E^)9
1 OE-05
4 5E 08
23E-10
NT
NT
5 2E 03
7 9E 08
30E^)5
9 5E 07
15E4)4
1 3EX)7
51E^)3
NT
NT
NT
NT
                                                                                                                                   Total HI   1 3E-02   4.7E4>2   2 BE 02    1 3E 02
  im« V. Appendix V-17
-------
                            APPENDIX V-18

                Estimation of Cancer Risks and Hazard Quotients
                  for Subsistence Fisher and Local Deer Hunter
Volume V
-------
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-------
f ABLE 2 Ma* Ppm Hunlni an
-------
                           APPENDIX V-19



                        Estimation of Population Risk
Volume V
-------
Age-distributed Population
by ZIP Code
ZIP Code
43920
15059
15043
26034
26050
43968
44432
44455
44441
16115
15010
15052
15077
15050
26047
Population
Infants
364
84
42
66
24
112
157
20
32
41
386
35
3
43
60
Children
4.399
1,027
532
956
365
1,455
1,999
264
416
571
4,771
480
41
551
880
Adults
21.205
5.355
2.234
4.945
1.927
6,762
9.037
1,110
1.813
2,786
25.468
2,403
182
2.339
4.838
Source: CACI 1991
Volume V
Appendix V-19
-------
Fraction of ZIP Code Areas Contained within
VVTI Phase II Risk Assessment Suhareas
ZIP Code
43920
15059
15043
26034
26050
43968
44432
44455
44441
16115
15010
15052
15077 ..
15050
26047
Fraction of Zip Code Area Contained within Subarea
El
0.02
0.02
0.01
0
0
0
0
0
0
0
0
0
0
0
0
E2
0
0.19
0.23
0
0
0
0
0
0
0
0
0
0
0
0
E3
0
0.29
0.11
0
0
0
0
0
0
0
0
0.56
0.88
0.24
0
Nl
0.06
0
0
0
0
0
0
0
0
0
0
0
0
0
0
N2
0.24
0.10
0
0
0
0
0
0
0
0
0
0
0
0
0
N3
0.35
0.40
0
0
0
0
0.01
0.02
0.13
0.01
0.01
0.02
0
0
0
SI
0
0
0
0.13
0
0
0
0
0
0
0
0
0
0
0
S2
0
0
0.06
0.46
0.01
0
0
0
0
0
0
0
0
0
0
S3
0
0
0.24
0.40
0
0
0
0
0
0
0
0
0
0.06
0.26
Wl
0.06
0
0
0
0
0
0
0
0
0
0
0
0
0
0
YV2
0.17
0
0
0.01
0.79
0.03
0
0
0
0
0
0
0
0
0
W3
0.09
0
0
0
0.20
0.52
0.01 -
0
0
0
0
0
0
0
0.14
Notes-
Traction of ZIP code area within a siibaren was estimated hjised on Figure VIII-2, which was developed by superimposing suhnrcn l>omid;m<-s on a XII1
Code map of the Penns)|vanm, Ohio, and West Virginia area
Volume V
Appendix V-19
-------
                              REFERENCES
 CACI Marketing, Inc. (CACI).  1991.  The sourcebook of ZIP code demographics  Census
       edition, Volume one.  CACI, Marketing Systems.  Arlington. Virginia.
Volume V
-------
                             APPENDIX V-20

                Estimation of Cancer Risks and Hazard Quotients
                       Resulting from Fugitive Emissions
Volume V
AnnpnHiv V-Tl
-------
CASTFRN SECTOR A VI n/UlF INHALATION
int. ii
CAB SYSTEM

1 li«Mim,al
Acetonp
Actylonilnle
Caibnn Oisulhde
C arbon letiachlonde
1 2 Dibtomoethane
1 1 Uichlotoethenp
Formaldehyde
Hydfazme
? rjilropiopane
Pyndme
Dichln'odifluoromethane
Total RisWHI
WASTEWATER
TANK

Chemical
Acetone
Acrylomtnle
Catbon Oisulfide
Carbon Tetfachlonde
1 2 Dibfomoethane
1,1 Uichloioethene
f oimaldehyde
Hydrazme
2 Niliopropan*
Pyndme
Oichlmodifluoiomethane
Total Risk/Hi
TRUCK WASH

Chemical
Acetone
Acrylomtnle
Carbon Disulfide
Carbon Tetrachlonde
1 ? Dibromoelhane
1 1 Dichlofoethene
F ormaldehyde
Hydraztne
2 Nitiopropane
Pyndme
Dichlorodilluofomethane
Total Risk/Hi
TANK FARM

Mpmiral
Acetone
\cfylomtrtle
arbon Disulddp
arbon Tetrachlorid?
2 Uibromoethane
1 Picriloioelhene
ormaldehyde
fydra?me
' Nitropropane
Vidme
ot.ll RisMHI
Slope
Factor
(rng/kg d)
NA
0 24
NA
0053
0 76
1 2
0045
17
P4
NA
% lolal Ml

Inhal
Slope
Factor
(mg/kq d)
NA
024
NA
0053
0 76
1 2
0045
17
94
NA
% total HI
Inhal
Slope
Fractof
(mg/Vg d)
NA
024
NA
0053
0 76
1 2
0045
17
94
NA
% total HI
\
Inhal
Slope
(mg/Vg d)
NA
0 24
HA
n C53
0 76
1 2
0 045
17
94
NA


RA[
(uq'rnll
87 5
05
2 5
05
005
7 9
175
NA
5
0875
008



RAC
(ug/m3)
87 5
05
25
05
005
79
175
NA
5
0875
008

RAC
(ug/ml)
875
05
25
05
005
7 9
175
NA
5
0875
008


RAC
(ug/ml)
875
05
2 5
05
OPS
7 9
175
NA
5
0875
0 H8
Inhalation
RID
(rug/kg d|
25F 02
1 4E 04
7 IE 04
1 4E 04
1 4E 05
23E 03
50E 02
OOE'OO
1 4E 03
25E 04



Inhalation
RID
(mg/kg d)
25E02
1 4E 04
7 1E04
1 4E 04
1 4E 05
23E 03
50E02
OOE'OO
1 4E 03
25E 04


Inhalation
RID
(mg/Uq d)
25E 02
1 4E 04
7 1E04
1 4E 04
1 4E05
23E 03
50E02
OOE»00
1 4E-03
25E 04



Inhalation
RtD
(mg/kg d)
25E02
1 4E 04
7 1E 04
1 4E04
1 4E05
23E 03
50E 02
OOE'OO
1 4E 03
?5E 04

Emission
Rale
(poMire
[mq/kq d) (mg/kgd)
9 OE 08 5 4E 08
2 OE 09 1 2E 09
5 9E 09 3 6E 09
4 OE 09 2 4E 09
20E 10 1 2E 10
5 BE 09 3 5E 09
4 9E 08 3 OE 08
1 3E 10 7 6E 11
1 6E 09 9 8E 10
2 1 F 09 1 2E 09


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
1 1E08 68E07
2 5E 08 1 5E 08
7 5E 08 4 5E 08
5 OE 08 3 OE 08
2 5E 09 1 5E 09
7 3E 08 4 4E 08
6 2E 07 3 8E 07
1 6E 09 9 6E 10
2 1E 08 1 2E 08
2 6E 08 1 6E 08


Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
4 8E 08 2 9E 08
1 1E 09 6 4E 10
3 2E 09 1 9E 09
21E09 13E09
1 1E 10 64E 11
3 1E 09 1 9E 09
2 7E-08 1 6E 08
68E 11 4 1E-11
88E 10 53E-10
1 1E 09 68E 10


Cancer Cancer
Child School age
(mg/kg d) (mg/kg d)
4 6E 06 2 8E 06
1 OE 07 6 2E 03
3 1E 07 1 9E 07
2 1E 07 1 2E 07
1 OE 08 6 1E 09
30E07 1 BE 07
2 6E 06 1 5E 06
6 5E 09 3 9E 09
8 5E 08 5 1E 08
1 1F 07 f, V OU


Adult
Exposure
(mg/kg d)
2 BE 07
6 2E 09
1 BE 08
1 2E08
6 IE 10
1 8E 08
1 5E07
39E 10
5 IE 09
64E 09


Noncancer
Adult
Exposure
(mg/kg d)
3 5E-06
78E08
23E07
1 6E 07
77E09
23E07
1 9E-06
50E09
64E 08
B2E 08


Adult
Exposure
(mg/kg d)
1 5E07
33E09
1 OE08
87E09
33E 10
9 BE -09
8 3E-08
21E-10
2 8E-09
3 5E 09


Noncancer
Adult
(mg/kg d)
1 4E05
32E 07
96E 07
6 4E 07
3 2E 08
94E 07
80E 06
20E08
26E 07
3 V 07


C hild School age
Exposure Fxpo-.ure
(rnglkq d) (mg/kg d)
1 OE 06 6 3E 07
2 3E 08 1 4E 08
6 9C 08 4 2E 08
4 6E 08 2 BE 08
2 3E 09 1 4E 09
6 BE 08 4 1E 08
5 7E 07 35E07
1 5E 09 8 8E 10
1 9E 08 1 1E 08
2 4F 08 1 5E 08


Noncancer Noncancef
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
1 3E 05 8 OE 06
2 9E 07 1 8E 07
8 7E 07 5 3E 07
5 9E 07 3 5E 07
2 9E 08 1 7E 08
8 6E 07 5 2E 07
7 3E 06 4 4E-06
1 9E-08 1 1E 08
2 4E 07 1 5E 07
31E07 18E07


Child School-age
Exposure Exposure
(mg/kg d) (mg/kg d)
5 6E 07 3 4E 07
1 2E 08 7 5E 09
3 7E 08 2 3E 08
2 5E 08 1 5E 08
1 2E 09 7 4E-10
3 7E 08 2 2E-08
3 1E 07 1 9E-07
79E 10 48E-10
1 OE 08 6 2E 09
1 3E 08 7 9E-09


CAB
Adult
( ancer
Risk
0
?E 10
0
8E 11
6E 11
3E 09
9E 10
9E 10
6F09
0

1 1E-08
WW Tank
Adult
Cancer
Risk
0
2E09
0
1E 09
8E-10
4E08
1E-08
1E 08
8E 08
0

1 4E-07
Adult
Cancer
Risk
0
1E 10
0
5E-11
3E 11
2E09
5E 10
5E 10
3E09
0

SOE-09
Noncancer Noncancer Tank Farm
Child School age
(mq/kg d) (mg/kg d)
5 4E 05 3 3E 05
1 2E 06 7 2F 07
3 6E 06 2 2E 06
2 4F 06 1 5F Of,
1 2E 07 7 1[ 08
3 5E 06 2 IF 06
3 OE 05 1 8F. 05
7 6E 08 4 6F 08
° 9E 07 6 OF 07
1 2F 0<5 7 5F 07

Adult
Risk
0
1F 08
0
4F 09
JE 09
1E 07
•JF 08
4F 08
'!F  7f 07
CAB
Child
C.incer
Risk
0
sr: 10
0
2E 10
1E 10
7E 09
2E09
2E 09
2F 08
0

27E-08
WWTank
Child
Cancer
Risk
0
6E-09
0
3E09
2E-09
9E-08
3E08
3E08
2E07
0

35E-07
Child
Cance
Risk
0
3E 10
0
1E 10
8E 11
4E09
1E09
1E 09
BE 09
0

1 SE^JB
Tank Farm
Child
( AH
Sf hool age
Cancer
Risk
0
3E 10
0
1E 10
9E 11
4E 09
1E09
1E 09
9F 09
0

1 7E-08
WWTank
School age
Cancer
Risk
0
4E09
0
2E09
1E09
5E08
2E08
2E08
1E 07
0

2 1E-07
School-age
Cancer
Risk
0
2E 10
0
7E-11
5E 11
2E09
7E 10
7E 10
5F 09
0

90E-09
Tank Farm
School age
Risk R.sk
0
2F 08
0
1F 08
'!( (I'l
41 07
If 07
IF rj?
i'l "I
'
1 4F OG
0
IF on
0
n fn
r,i n'i
2! II!
71 0>)
/I 01
',1 'i/
',
n <>r 07
CAR
Adult

Child School age
Jonr.incer IJoncaricer NoiK-.-iruer
HO
1E 05
4F; 05
3E 05
9E 05
4E 05
BE 06
IE 06
ERR
4E 06
3E 05
2E 05
2 7E-04
WW Tank
Adult
Noncancer
HQ
IE 04
5E-04
3E 04
1E 03
5E04
1E04
4E 05
ERR
5E05
3E04
3E 04
34E-03
Adult
Noncancer
MQ
6E06
2E 05
1E 05
5E05
2E05
4E06
?E06
ERR
2E 06
1F 05
IE 05
1 5E 04
lank Farm
Adult
HO
r, 04
.' in
1 'n
', o i
/ ': ',
i 'it
.' '14
I'l'
''4
l '; '
1 ', '
1 4 07
HQ HO
4E 05 3E 05
2F 04 1t 04
1E 04 6E 05
3E 04 2E 04
2E 04 1E 04
3E 05 2E 05
1E05 7E06
ERR snn
1E05 BE 06
IE 04 6E 05
7E 05 5E 05
1 OE-03 6 1E-04
WW Tank WW Tank
Child School age
Noncancer Noncancer
HQ 1 IQ
5E 04 3E 04
2E 03 1E 03
1E03 7E04
4E 03 2E 03
2E03 1E03
4E 04 2E 04
1E04 9E-05
ERR ERR
2E 04 IE 04
IE 03 7E 04
9E 04 6E 04
1 3E-02 7 7E-03
Child School age
Noncancer No|K.ari( 3
11 '. : 'A '] ;
1 ?F 0? 1 7F 0?
»rr""dix V 20
-------
WESTERN SFCTOR

cnn '. i ',IIM

( hpiTnr.ll
Acplone
Actytonilnle
Carbon Oisullide
Carbon Tptrachlonde
1 2 Oibromoethane
1 1 Dichloroethene
F ortTialdehyde
Mydra/me
2 Nitropropane
Pyildme
Oichlotodifluoromethane
Total Risk/Hi
WASTEWATER
TANK

Chemical
Acetone
Acrylomtrile
Carbon Disullide
Carbon Tetrachlonde
t 2 Dibromoethane
1 1 Oichloioethene
f ormaldehyde
Mydrazrne
2 Nrtropropanp
Pyndme
Die h lorod if luo iom ethane
Total Risk/Hi
TRUCK WASH


Chemical
Acetone
Acrylonitnle
"arbon Disultide
~arbon Telrachlonde
I 2 Dibiomoethane
I 1 Dichloroethene
ormaldehyde
lydrazine
> Nitropropane
'yndine
lichlorodifluoromethane
otal Risk/Hi
ANK FARM


hernical
cetone
uylonitlrle
.iibon DisultidP
aibon letiachioiide
T pihiomoelhane
1 [)ichloioethene
vmaldphyde
ydra^me
Niliopiopaoe
iridme
hl'iinlilluornmelhanp
->l.ll Risk/Hi
.C INHAI ATION
Inli It
Slope
! act™
(mg/kg d) t
MA
0 24
NA
0053
0 76
1 2
0045
17
9 4
MA
% total Ml =

Inhal
Slope
Factor
(mg/kg d) 1
NA
0 24
NA
0053
0 76
1 2
0045
17
94
NA
% lolal Ml -

Inhal
Slope
Factor
(mg/kg d) 1
NA
024
NA
0053
0 76
1 2
0045
17
94
NA
% total Ml =

Hihal
Slope
Factor
[mg'kg d) 1
NA
0 JJ
NA
0053
0 76
1 2
0045
17
1 4
NA
% I',' 11 Ml -



RAC
(uq/r..1|
87 5
05
25
05
005
7 9
175
NA
5
0875
008



RAC
(ug/m3)
875
05
25
05
005
79
175
NA
5
OP7S
OOH



F)AC
(uq'rnl)
875
05
25
05
005
79
175
HA
5
0875
008



RAC
(ug/m3)
87 5
05
25
05
005
7 9
175
NA
5
PP75
0 08


Inhalation
RID
(rnq/kg d)
25E 02
1 4E 04
7 1E 04
1 4E 04
1 4E 05
23E03
50E 02
OOE'OO
1 4E03
25E04



Inhalation
RID
(mg/kg d)
25E02
1 4E04
7 1E04
1 4E 04
1 4E 05
23E03
50E 02
OOE'OO
1 4E 03
2 5E 04



Inhalation
RID
(mg'lg d)
25E 02
1 4E04
7 IE 04
1 4E 04
1 4E-05
23E03
5 OE 02
OOE'OO
1 4E 03
25E 04



Inhalation
RID
|mg/kg d)
25E 02
1 4E 04
7 1E 04
1 4E 04
1 4E 05
23E 03
50E 02
OOE'OO
t 4E 03
25E 04



Emission
Rate
(g/spc)
1 23E 03
271E OS
8 1E 05
5 44E 05
2 68E 06
7 95E 05
6 75E 04
t 72E 06
2 23E 05
2 83E 05



Emission
Rale
(g/sec)
1 10E 03
244E05
73E05
490E05
241E 06
7 16E 05
6 08E 04
1 55E 06
201E 05
2 55F 05



Emission
Rale
(g/ser)
5 4 1 E 05
1 19E 06
36E 06
240E06
1 18E07
351E08
2 98E 05
758E 08
9 86E 07
1 25E 06



Emission
Rate
(g/s»c)
1 16E 02
257E04
7 7E 04
5 16E 04
2 54E 05
7 54E 04
6 40E 03
1 63E 05
2 1 2E 04
2 68E 04


A.ql\psl
V.ipor
or
(ug/ml qlt)
064
064
064
064
064
064
064
064
064
064


Avg West
Vapoi
DF
(ug/m3 g/s)
9 7
9 7
9 7
9 7
9 7
9 7
9 7
9 7
9 7
Q >


A,g WfSl
V.ipor
Df
(ugiml g/5)
14
14
14
14
14
14
14
14
14
14


Avg West
Vapor
DF
lug/ml 4q/s)
208
208
208
208
208
208
208
206
208
20 a


Avg WPS!
nf) Site
Cone
(uq/ml)
00008
OOOOO
00001
OOOOO
OOOOO
OOO01
00004
OOOOO
OOOOO
OOOOO


Avg West
OH Site
Cone
(ug/m3)
00107
00002
00007
00005
OOOOO
00007
00059
OOOOO
00002
00002


Avg West
Oft Site
Cone
(ug/m3)
00008
OOOOO
00001
OOOOO
00000
OOOOO
00004
OOOOO
OOOOO
OOOOO


Avg West
Of) Site
Cone
jug/m3)
00603
00013
00040
00027
0 0001
00039
00333
00001
00011
0 0014


Cancpr
Adult
Fxposute
(mg/kg d|
2 BE 08
6 IE 10
1 8E 09
1 2E 09
60E 11
1 8E 09
1 5E 08
39E 11
50E 10
64E 10


Cancel
Adult
Fxposurp
{rng/kg d)
38E 07
83E 09
25E 08
t 7E 08
82F 10
24E08
21E07
53E 10
69E 09
8 7E 09


Cancel
Adult
Exposure
(mg/kg d)
2 7E 08
59E 10
1 8E 09
1 2E09
58E 11
1 7E09
1 5E08
37E 11
49E 10
62E 10


Cancer
Adult
Exposure
(mg/Vg d)
2 1E06
4 7C 08
1 4E 07
9 3 7E 05
1 4F 06 8 3E 07
4 It 06 2 5F 06
2 71 00 1 7E Of.
1 4f 07 8 2F 08
4 OF 06 2 4F 06
34F05 2 IE 05
8 7F 08 5 2F Ofl
1 1C 06 0 8( 07
1 4F 06 8 <5F 07


CAR
Adull
Cnm.pi
Risk
0
1E 10
0
6E 11
5E 11
2E09
7E 10
7C 10
5F 09
0

85E-09
WWTank
Adult
Cancer
Risk
0
2E09
0
9E-10
6E 10
3EOS
9E09
9E09
6F 08
0

1 2E-07
Ttuck
Adult
Cancer
Risk
0
1E 10
0
6E 11
4E 11
2E09
7E 10
6E 10
5F09
0

B2E-09
Tank Farm
Adult
Cancer
Risk
0
IF 08
0
y 8
WWTank WW Tank
Child School age
Cancer Cancer
Risk Risk
0 0
5E 09 3E 09
0 0
2E 09 1E 09
2E 09 9E 10
7E 08 4E 08
2E 08 1E 08
2E08 IE 08
2E 07 1E 07
0 0

2 9E-07 1 7E-07
Ttuck Tiuck
Child School age
Cancer Cancer
Risk Risk
0 0
4E 10 2E 10
0 0
2E-10 9E11
1E10 7E-11
5E 09 3E 09
2E09 1E09
2E 09 1E 09
1E08 7E09
0 0

2 OE-OB 1 2E-08
Tank Farm Tank Farm
Child School age
Cancel Cancer
Ri-.k Rr.k
0 0
IF OH 2( 08
0 0
1! OH 81 O'l
9( D') 5( O'l
4F 07 ?( 07
1F 07 HI oa
11 D7 HI 1)11
"I "/ ',( '!/
'

1 r.r Of, 9 RF 07
( AB
Adult
Uoncancei
HQ
9E06
3E05
2E 05
7E 05
3E05
6E06
2E06
ERR
3E-06
2E05
?E 05
2 1E-04
WW Tank
Adult
Noncancer
HQ
1E 04
5E04
3E04
9E 04
4E 04
8E05
3E 05
ERR
4E 05
3E04
2E04
2BE-03
Tiuck
Adult
Noncancer
HQ
BE 06
3E05
2E 05
6E05
3E05
6E06
2E06
ERR
3E06
2E 05
1F 05
20E-04
Tank f arm
Arlilll
MnnraruM
Mr)
7F F)4
II 0!
,'l 0!
',( II!
! 'i :
', 'J4
.' f|4
I'fJ
.' M

1 ', <
t <; o?
( AB
Child
t lone. UK et
HO
3E 06
1E 04
7E 05
2E 04
1E 04
2E 05
9E06
ERR
1E05
7E05
6E 05
7 BE -04
WW Tank
Child
Noncancei
HQ
4E04
2E03
1E 03
3E 03
2E 03
3E 04
1E 04
ERR
1E04
1E 03
BE 04
1 1EO2
Tiuck
Child
Noncar cer
HQ
3E 05
1E 04
7E05
2E 04
1E04
2E 05
9E06
ERR
1E05
7f 05
6F 05
7 5E 04
Tank F arm
r inH
ll'lll' ."HIM
MQ
21 1)1
IF 02
61 )!
A U
nr.-»ntpr
MQ
1F 03
61 03
IF 0)
11 1)2
',1 Hi
IF 0!
4F_ 0/1
( nil
M (14
!l 01
II '}'.
i <;r m
-------
NORTHERN SECTOR  - AVERAGE IHHAl ATION

CAB SYSTEM

Chemical
Acetone
Acrylomtnle
Carbon Disulfide
Carbon Tetrachlonde
1 2 Fjibromoethane
1 1 Dichloroethene
Formaldehyde
Hydrazme
2 Nilropropanp
Pyndine
Uichlorodrlluoromethane
Total Risk/Hi
WASTEWATER
TANK

Chemical
Acetone
Acrylonitfile
Carbon Drsuldde
Carbon Tetrachlonde
1 2 Dibromoethane
1 1 Dichloroethene
formaldehyde
Hydrazine
2 Nitropropanp
Pyndine
Die hlorod if luoiom ethane
Total RIsWHI
TRUCK WASH


t hemical
Acetone
Acrylimtnle
Carbon Disullide
Carbon Tetrachlonde
1 2 Dibromoethane
1 1 Dichloroethene
Formaldehyde
Hydrazme
2 Nitropropane
Pyndine
Dichlofodifluoromethane
Total RIskJHI
TANK FARM


Chemical
Acetone
•\crylnmtiile
athon Disulfide
aibon Tptiarhlo'idp
1 I1 F)ibiornoethane
! 1 Oichloroethpne
ormaldehyde
lydra?me
1 MitiopiopaMp
Vid'"P
'i, iilMiodtfluoiO'Tislhanp
ottl Risk/Hi
Inhal
Slope
f actor
(mg/kg d) 1
MA
024
NA
0053
0 76
1 2
0045
17
9 4
NA
% tola! HI -

Inhal
Slope
Factor
(mg/kg d) 1
NA
024
NA
0053
0 76
1 2
0045
17
9 1
NA
% lotal HI -

Inhal
Slope
1 actor
(mg/kg d| 1
NA
024
NA
0053
0 76
1 2
0045
17
94
NA
% total HI =
^
Inhal
Slope
Factor
(mg/kg d) 1
NA
P 24
NA
OP53
n 76
1 2
0045
17
9 4
MA
% total HI -



RAC
lug/ml)
HI 5
05
25
05
005
7 9
175
NA
5
0875
008



RAC
(ug/m3)
875
05
25
05
005
79
175
MA
5
0875
008



RAC
lug/ml)
87 5
05
25
05
005
7 9
175
NA
5
0875
008



RAC
(ug/m3)
875
05
2 5
05
005
79
175
NA
5
P P75
008


Inhalation
RIU
(mg/kg d)
25E 02
1 4E 04
7 1E 04
1 4E 04
1 4E05
23E 03
50E 02
OOE'OO
1 4E03
25E 04



Inhalation
RID
(mg/kg d)
25E02
1 4E04
7 IE 04
1 4E 04
1 4E 05
23E03
50E 02
OOE'OO
1 4E 03
25F 04



Inhalation
RID
(mg/kg d)
25E 02
1 4E 04
7 1E04
1 4E04
1 4E05
23E03
50E02
OOE'OO
1 4E 03
25E04



Inhalation
RID
(mg/kg d)
25E02
1 4E 04
7 1E 04
1 4E 04
1 4E 05
2 3E 03
50E 02
OOE-00 "
1 4E 03
25E 04



F mission
Rate
(g/spc)
1 23E 03
2 71E 05
8 1E 05
5 44E 05
2 68E 06
7 95E 05
6 75E 04
t 72E 06
2 23E 05
2 83E 05



Emission
Rate
(g/sec)
1 IDE -03
2 44E 05
73E05
4 90E 05
241E 06
7 16E 05
6 QBE 04
1 55E 06
2 DIE 05
J 55F 05



F mission
Rate
Ig'SPc)
541E 05
1 19E 06
36E 06
240E06
1 18E 07
351E06
2 98E 05
758E08
8 86E 07
1 25E06



Emission
Rale
(g/sec)
1 16E02
257E 04
7 7E 04
5 16E 04
2 54E 05
7 54E 04
6 40E 03
1 63E 05
2 12E 04
2 SflF 04


A^q North
Vapor
OF
(ug/ml q/s)
049
049
049
0 49
049
049
049
049
049
0 49


Avg North
Vapor
DF
(ug/m3 g/s)
153
153
15 3
15 3
15 3
15 3
15 3
15 3
153
15 1


Avg North
Vapor
DF
lug/ml g's)
15 1
15 1
15 1
15 1
15 1
15 1
15 1
151
151
15 1


Avg North
Vapor
DF
(ug/m3 4g/s)
104
104
104
104
104
104
104
104
104
10 4


A.g North
cm Site
Cone
(ug/ml)
00006
00000
00000
00000
00000
00000
00003
00000
00000
00000


Avg North
OH Site
Cone
lug/mil
00168
00004
00011
00007
00000
00011
00093
00000
00003
00004


Avg North
Oft Site
Cone
(ug'ml)
ooooa
00000
00001
00000
00000
00001
00004
00000
00000
00000


Avg North
Off Site
Cone
(ug/m1|
00302
00007
00020
00013
00001
00020
00166
00000
00006
00007


Cancpi
Adult
Fxpo°une
(mg/kg d)
2 1E08
4 7E 10
1 4E 09
94E 10
46E 11
1 4E 09
1 2E 08
30E 11
38E 10
49E 10


Cancer
Adult
Exposure
(mg/kg d)
59E07
1 3E 08
39E 08
26E08
1 3E 09
39E 06
33E 07
84E 10
1 1E 08
1 4F 08


Cancer
Adult
Exposure
(mg/kg d)
29E 08
63E 10
1 9E 09
1 3E-09
63E 11
1 9E 09
1 6E 08
40E 11
52E 10
66E 10


Cancer
Adult
Exposure
(mg/kg d)
1 1E 06
2 4E 08
7 OE 08
4 7E C8
2 3E 09
6 9E 08
59E 07
1 5E 09
1 9E 08
? SF 08


Cancer Cancpr
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
5 3E 08 3 2E 08
1 2E 09 70E 10
35E09 2 IE 09
2 3E 09 1 4E 09
1 2E 10 70E 11
34E09 2 IE 09
2 9E 08 1 8E 08
7 4E 11 4 5E 1 1
96E 10 58E 10
1 2E 09 7 4E 10


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
1 5E-06 89E-07
3 3E 08 2 OE 08
9 8E 08 5 9E 08
6 6E 08 4 OE 08
3 2E 09 2 OE 09
9 6E 08 5 8E 08
8 2E 07 4 9E 07
2 IE 09 1 3E 09
2 7E 08 1 6E 08
34F 08 2 IF 08


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
7 2E 08 4 3E 08
1 6E 09 95E 10
4 7E 09 2 9E 09
3 2E 09 1 9E 09
1 6E 10 94E11
4 6E 09 2 8E 09
3 9E 08 2 4E 08
1 OE 10 6 IE 11
1 3E 09 79E 10
1 7E 09 1 OE 09


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d|
1 6E 06 1 6E 06
5 9E 08 3 5F 08
1 BE 07 1 1E 07
1 2E 07 7 1E 08
5 8E 09 3 5E 09
1 7E 07 1 OE 07
1 5E 06 88E 07
3 7E 09 2 2F 09
4 8E 08 29E 08
F W 41 0'!
41 m ''.( o't
?F 07 IF r)7
71 08 41 08
r,F r-J" 41 01
•r fi/ ',i i)7
' 'j

R IF 07 4 9F 07
HO
7E06
3E 05
2F05
5E 05
3E 05
5E06
2E06
ERR
2E 06
2E05
1E05
1 BE -04
WW Tank
Adult
Noncancer
HQ
2E04
7E04
4E 04
1E 03
7E04
1E04
5E05
ERR
6E05
4E04
3E 04
4 5E-03
Truck
Adult
Noncancer
HQ
9E06
3E05
2E05
7E05
3E05
6E06
2E06
ERR
3E 06
2F 05
2E05
22E-04
Tank F aim
A'lull
Nonr ancei
MO
IF '14
IF 0!
ill 04
•I o :
11 ' 11
A 'A
'!( <>'
I 1(1'
11 ',1
;•! • 1
'.I ',4
R 'IF 01
HO HO
2E 05 1E 05
1E04 6E 05
6E 05 3E 05
2E 04 IF 04
9E 05 6E 05
2E05 1E05
7E 06 4E 06
ERR ERR
8E 06 5E 06
6E 05 3E 05
4E 05 3E 05
59E-O4 3SE-04
WW Tank WW Tank
Child School agp
Noncancer Noncancer
HO HO
7E 04 4E 04
3E 03 2E 03
2E 03 1E03
5E 03 3E 03
3E 03 2E 03
5E 04 3E 04
2E 04 IE 04
ERR ERR
2E04 IE 04
2E 03 1E03
1E 03 7E 04
1 7E-02 1 OE-02
Truck Fruck
Child School aqe
Noncancer Nonranrer
HO HO
3E 05 2E 05
1E 04 8E 05
BE 05 5E 05
3E 04 2E 04
IE 04 BE 05
2F 05 It 05
OE 06 6E 06
ERR EF*R
11 05 6E 06
8f 05 5F 05
61 05 4E 05
81E04 49F04
lank I .inn Fank F arm
r hiH School aqe
1 IOIH ,inf PI lloricancer
HO HO
II 01 71 04
',[ 0! 11 (13
!f 0! 2f 01
1[ Hi fit 0!
'.I 0! 11 Hi
')( 04 SF 04
M '14 21 04
1 HI) ( MR
4! '14 ?F 04
•1 ','. .'1 01
,'! ','. 11 01
1 01 0? 1 IF rj?
-------
SOUTHERN SFCTOR
CAB SYSTEM

Chemical
Acetone
Acrylonitnle
Carbon Drsullide
Carbon Tetrachlorrde
1 2 Dibromoethane
1 1 Dlchlotoethene
Formaldehyde
Hydrazme
2 Nrlropropane
Pyndme
Dichlorodifluoromethane
Total Risk/Hi
WASTEWATER
TANK

Chemical
Acetone
Aciylonttnle
GattJon Chsultide
Carbon Tetrachlonde
1 2 Dibromoethane
1 1 Dichloroelherie
^ormaldehyde
lydrazrne
1 Nitropropanp
'yndme
lichlorodifluoromplhnnp
'otal RKk/HI
RUCK WASH


hemical
cetone
-crytonitnte
arbon Disuifide
a'bon Tetrachlonde
2 Dibromoethane
1 Dichloioethene
ormaldehyde
ydrazrne
Nitropropane
yridine
ichlorodiHuoiomethane
Jlal RIsWHI
VNKFARM

|
1 lemical
1 ptone
lylonitnlp
rbon Disuifide
rbon Telrachlonde
' Dibromoethane
Oichloroetfipnp
irnaldphydp
drazine
Mropropane
limp
M'midilluo'-vnp'h.ji p
nl RiskJHI
f r ,, ,F, ifJHAI A1ION
Inli il
Slope
F tictor
(mq/kg d| 1
NA
0 24
NA
0053
0 76
1 2
0045
17
94
NA
\ total Ml -

Inhal
Slope
f actor
(mg/kg d) 1
NA
024
NA
0053
0 76
1 2
0045
17
14
NA
% totsl III -

Inhal
Slope
F actor
(mq/kg d) 1
NA
0 24
NA
0053
0 76
1 2
0045
17
94
NA
% total HI =

Inhal
Slope
Factor
(mg/kg d) 1
NA
0 24
NA
0053
P 76
1 2
mJ5
17
Q 4
N«
•^ tc'at Hi -


RAC
(ug/m3|
87 5
05
25
OS
005
79
175
(JA
5
0875
008



RAC
(ug/mS)
S75
05
2 5
05
005
79
175
NA
5
PP75
o rift



RAC
(ugiml)
875
05
25
05
005
79
175
NA
5
0875
008



RAC
(ug/ml)
87 5
0 5
25
0 5
r>05
7 9
175
fJA
5
PR75
0 08

Inhalation
RID
(mg/kg d)
25E 02
1 4E 04
7 1E 04
1 4E 04
1 4E 05
23E03
50E 02
OOE'OO
1 4E 03
25E04



Inhalation
RID
(mg/kg d)
25E02
1 4E04
7 1E04
1 4E04
1 4E05
23E 03
50E 02
OOE'OO
1 4E 03
25F 04



InhaUtion
RIO
(mglkg d)
25E02
1 4E 04
7 IE 04
1 4E04
1 4E 05
23E03
50E02
OOE'OO
1 4E-03
2 5E 04



Inhalation
RIO
{mg/kg d)
25E02
1 4E 04
7 1E 04
1 4E 04
1 4E 05
2 3E 03
5 OF 02
OOE'OO
1 4E 03
?5F 04


Emission
Rale
(g/sec)
1 23E 03
271E 05
81E 05
5 44E 05
268E O6
7 95E 05
6 75E 04
1 72E 06
2 23E 05
2 83E 05



Emission
Rate
(g'sec)
1 10E 03
2 44E 05
73E 05
4 90E 05
241E 06
7 16E 05
6 08E 04
1 55E 06
2 DIE 05
2 55E 05



E mission
Rale
(q«,-c)
541E 05
1 19E 06
36E 06
2 40E 06
1 18E 07
351E06
2 98E 05
7 58E 08
9 86E 07
1 25F 06



Emission
Rate
(q/sec)
1 16E 02
257E04
7 7E 04
5 16E 04
2 54E 05
7 54E 04
6 40E 03
1 63E 05
2 12E 04
? MF 04



V.ipor
or
fug/ml g/s)
066
066
068
066
066
066
066
066
066
066


Avg South
Vapor
DF
lug/ml g/s)
54
54
54
54
54
54
54
54
5 4
5 4


»«g South
Vapor
or
(ugrml gis)
6 3
6 3
6 3
63
63
63
63
63
63
6 3


A jg South
Vapor
Of
(ug/ml 4g/s|
162
162
162
162
16 2
16 2
16 2
16 2
16 2
16 2



Off Sile
Cone
(<;g/m1)
00008
OOOOO
00001
OOOOO
OOOOO
00001
00004
OOOOO
0 0000
OOOOO


Avg South
Off Sile
Cone
|iig/m3)
00059
00001
00004
00003
OOOOO
00004
00033
OOOOO
00001
00001


Avg South
Otl Site
Cone
(..gfml)
00003
OOOOO
OOOOO
OOOOO
OOOOO
OOOOO
00002
ooooo
OOOOO
OOOOO


Avg South
Oft Site
Cone
(ug/ml)
00470
00010
00031
00021
00001
00031
00259
00001
00009
0 r>OH



Adull
Exposure
(mg/kg d)
29E 08
63E 10
1 BE 09
1 3E 09
62E 11
1 8E09
1 6E 08
40E 11
52E 10
66F 10


Cancer
Adult
Exposure
(mg/kg d)
21E07
46E09
1 4E 08
93E09
46E 10
1 4E08
1 2E07
29E 10
3 BE 09
4 8E 09


Cancer
Adull
Exposure
(mg/kg d)
1 2E08
26E 10
79E 10
53E 10
26E 11
78E 10
66E09
1 7E-11
22E 10
2 BE 10


Cancer
Adult
Exposure
(mg/kg d)
1 7E06
3 7E 08
1 1E 07
7 4E 08
36E09
1 1E 07
9 IE 07
2 3E 09
3 OE 08
1 8F 0«



Child S( hool age
Exposure Exposure
(mg/kg d) (mg/kg d)
7 IE 08 4 3E 08
1 6E 09 95E 10
4 7E 09 2 BE 09
3 1E 09 1 9E 09
1 6E 10 94E 11
4 6£ 09 2 8E 09
3 9E 08 2 4E 08
1 OE 10 60E 11
1 3E 09 7 8E 10
1 6F 09 9 9F 10


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) |mg/kg d)
52E07 31E07
1 2E 08 7 OE O9
35E08 21E08
2 3E 08 1 4E 08
1 1E 09 69E 10
3 4E 08 2 OE 08
29E 07 1 7E 07
7 3E 10 4 4E 10
9 5E 09 5 8E 09
1 2F 08 7 IF 09


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
3 OE 08 1 8E 08
66E 10 40E 10
2 OE 09 1 2E 09
1 3E 09 8 OE 10
6 5E 1 1 3 9E 1 1
1 9E 09 1 2E 09
1 6E 08 1 OE 08
4 2E 11 25E 11
54E 10 33E-10
69E 10 4 2E 10


Cancef Cancer
Child School age
Exposure Exposure
(mq/Vq d) (n,g/kg d)
4 IE 08 25EQ6
9 IE 09 5 5E 08
2 7E 07 1 6E 07
1 8E07 1 1E 07
9 OE 09 5 5E 09
2 7E 07 1 6E 07
2 3E 06 1 4E 06
5 8E 09 3 5E 09
7 5E 09 t OF 09
o 5F 'll '• "F "R



Adult
Exposure
(rng/kq d)
22E 07
4 9F 09
1 5E 08
98E 09
4 BE 10
1 4E 08
1 2E07
3 1E 10
40E 09
5 IF 09


Noncancer
Adult
Exposure
(rng/kg d)
16E06
36E08
1 IE 07
72E08
36E09
1 1E07
90E07
23E09
30E 08
38F 08


Noncancef
Adult
Exposure
(mg/kg d)
93E08
2 IE 09
62E09
4 IE 09
20E 10
61E09
5 IE 08
1 3E 10
1 7E09
22E09


Honcancer
Adult
Exposure
(mg/kg d)
1 3E05
29E 07
85F 07
5 7F 07
2 BE 08
9 4E 07
7 1E 06
1 9F 08
24F 07
1 'If 07



Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
8 3E 07 5 OE 07
1 BE 08 1 IE 08
5 5E 08 3 3E 08
3 7E 08 2 2E 08
1 8E 09 1 1E 09
5 4E 08 3 2E 08
4 6E 07 2 8E 07
1 2E 09 7 OE 10
1 5E08 9 1E09
1 9E 08 1 2E 08


Noncancer Noncancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
61E06 37E06
1 3E 07 8 1E 08
4 OE 07 2 4E 07
2 7E 07 1 6E 07
1 3E 08 8 OE 09
4 OE 07 2 4E 07
3 4E 06 2 OE 06
8 6E 09 5 2E 09
1 1E 07 6 7E 08
1 4E 07 8 5E 08


Noncancm Noncancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
35E-07 21E07
7 7E-09 4 6E 09
2 3E 08 1 4E 08
1 5E-08 9 4E 09
76E10 46E-10
2 3E 08 1 4E 08
1 9E-07 1 2E 07
49E-10 30E10
8 4E 09 3 8E 09
81E09 49E09


Noncancer Noncancer
Child School age
Exposure Exposure
(mg/kg d) (mq/kg d)
4 <)E 05 2 9E 05
1 IE 06 64F 07
3 2E 06 1 V 06
2 1C 06 1 IF 06
1 IE 07 64F 08
1 1 f 06 1 9F 06
2 7E 05 1 6E 05
68E 08 4 1F 08
89E 07 5 IF 07
1 1f 00 6 l\ 'I?


CAB
Adull
Cancer
Risk
0
2F 10
0
7E 11
5E 11
2E09
TE 10
7E 10
5E09
0

87E-09
WW Tank
Adult
Cancer
Risk
0
1E09
0
5E 10
3E 10
2E08
5E09
5E09
4E 08
0

64E-OB
Truck
Adult
Car cer
Risk
0
6E 11
0
3E 11
2E 11
9E 10
3E 10
3E 10
2E 09
0

37E-09
lank f arm
Adult
Cancel
Risk
0
'>[ 09
0
IF 09
3E O'J
IF 07
IF 08
•IF 08
"1 rif


' IF 07
f AR
L-'Atl
Child
Cancel
Risk
0
4F 10
0
2E 10
1E 10
6E09
2E09
2E09
1F 08
0

22E-08
WW Tank
Child
Cancer
Risk
0
3E09
0
1E09
9E 10
4E08
IE 08
IE 08
9E 08
0

1 6E-07
Truck
Child
Cancer
Risk
0
2E 10
0
7E 11
5E 11
2E 09
7E 10
7E 10
5E 09
0

92E-09
lank Farm
Child
Cancel
Risk
0
?F 08
0
IF 08
7F ')<)
•1 07
11 07
11 ')/
n ' /
rj

1 IF Of,

School age
Cancer
Risk
0
2E 10
0
1E 10
7E 11
3E09
1E 09
IE 09
7E09
0

1 3E-08
WWTank
School age
Cancer
Risk
0
2F09
0
7E 10
5E 10
2E08
8E 09
BE 09
5E08
0

97E-OB
Truck
School-age
Cancer
Risk
0
1E 10
0
4E 11
3E 11
1E09
4E 10
4E 10
3E 09
0

55E-09
Tank F arm
Srhool age
Cancer
Risk
0
IF 08
0
01 ')9
IF O'J
2F 07
OF O'l
0( ')')
11 ')/
'

7 7F 07

Adult
Noncancer
HQ
9E 06
3E 05
2E 05
7EOS
3E05
6E06
2E06
ERR
3E06
2E05
2E05
21E-04
WW Tank
Adull
Noncancer
HQ
7EOS
3E04
2E04
5E04
2E04
5E05
2E 05
ERR
2E05
2E04
1E04
1 6E-03
Truck
Adull
Noncancer
HQ
4E06
1E05
9E06
3E 05
1E05
3E 06
IE 06
ERR
IE 06
9F 06
7E 06
90E-05
lank 1 arm
Ariull
1 lonr ancfl
HO
ri( 04
?l 01
11 'I!
41 ')',
1\ <>':
11 'i1
l( '11
( I'll
/I '/I
11 ')'.
'•I ')4
1 ?F 0?

Child
Noncaricei
MQ
3E 05
IE 04
BEOS
3E 04
1E04
2E05
9E06
ERR
1E05
8E05
6E05
BOE-04
WWTank
Child
Noncancer
HQ
2E04
9E04
6E 04
2E03
9E04
2E04
7E05
ERR
BEOS
6E04
4E 04
59E-03
Truck
Child
Noncancer
HO
1E05
5E05
3E05
IE 04
5E OS
11:05
-IE 06
ERR
4E 06
3F 05
2( 05
34E04
lank I arm
1 Vlllrl
Hour arne
HO
n 01
71 01
*( m
11 02
/f '))
11 ')•)
'rf '14
1 UK
',1 04
11 ')',
;l '/!
4 7f 07
( An
School agr
Noncaricei
MQ
2E 05
BE 05
5E05
2E04
8E05
1E05
6E06
ERR
6E 06
5E05
4E 05
48E-04
WW Tank
School age
Noncancer
MQ
1E 04
6E 04
3E 04
IE 03
6E 04
1E04
4E05
ERR
5E05
3E 04
3E 04
3 6E 03
Truck
School age
Honcancer
HQ
8F. 06
IE 05
2E 05
7E 05
3E05
6E 06
2E 06
ERI)
3E 06
2F 05
21 05
? OE 04
lank ( arm
">( ti'iil age
tl.mranrer
HQ
1( 01
1! 01
IF 01
'II 01
4! 01
81 04
If 04
f F)l(
1f 04
•I 'It
Ji 01
7 RF 0?
-------
MAX INHALATION
CAB SYSTEM

- l,pm,r.,l
Acptone
Ariylomtnle
Carbon Disullide
t a'bon Tetrachlonde
1 2 Dibromoethane
1 1 Dichloroethene
Formaldehyde
Hydrazine
2 Nifropropanp
Pyridme
Dichlorodifluoromelha
Total Risk/Hi

WASTEWATER
TANK
Chemical
Acetone
Acrylomtnle
Carbon Disulfide
Carbon Tetracblonde
1 2 F)ibromoethane
1 1 Dichloroethene
Formaldehyde
Hydiazme
2 Nitropropane
Pyndine
Dichloroditluoromptha
Total RiskJHI

TRUCK WASH
hemical
^etone
^tylonitnle
^aibon Disultide
"aibon Tetiachlonde
1 2 Dibromoethane
1 1 Dichloroethpne
ormaldehyde
tydrazine
' Nitropropanp
^yndine
Jichlorodilluorometha
otal Risk/Hi

ANK FARM
hemical
( plone
culonitnle
,ubon Disullide
aibon Tptrachloridp
2 Dibrornopthane
> Dichloroefhpne
oimaldehydp
ydrazme
Nitropropanp
>Mdme
ichlorodifluorornefha '
otal RiskJHI

Inh il
'"lotx-

(mg/kg d) 1
NA
0 24
NA
0053
0 76
0091
0045
17
94
NA
% total Ml =


Inhal
Slope
Factor
(mg/kg d) 1
NA
0 24
MA
0053
0 76
0091
0 045
9 4
NA
% total HI - % tots


Inhal
Slope
Factor
(mg/kg d) 1


(iiq/mlj
"75
05
2 5
05
005
125
175
NA
5
0875
008


RAC
(ug/m3)
875
05
25
05
005
125
175
f(A
5
0875
1 Ml -


RAC
(ug/m3)
NA 875
024 05
NA 25
0 053 05
0 76 0 05
0091 125
0045 175
17 NA
94 5
NA 0875
% total HI = % total HI =

y
Inhal
Slope
Factor
(mg/kg d) 1
NA
0 24
NA
0053
0 76
0091
0045
17
94
NA
t Ma' "1 - % total




RAC
875
05
2 5
05
005
125
175
NA
5
0875
Ml -



ion
RIU
(rrig/kg d|
25E 02
1 4E 04
7 1E 04
t 4E 04
1 4E 05
36E 02
50E 02
OOE'OO
1 4E03
25E04


Inhalation
RfD
(mg/kg d)
25E02
1 4E04
7 tE04
1 4E 04
1 4E 05
36E 02
50E 02
OOE<00
1 4E 03
25E 04


Inhalation
RID
(mg/kg d)
25E02
1 4E 04
7 1E 04
1 4E 04
1 4E 05
36E02
50E02
OOE»00
1 4E03
25E04


Inhalation
RID
(mg/kg d)
25E02
1 4E 04
7 1E 04
1 4£ 04
1 4E 05
36E 02
50E02
OOE'OO
1 4E 03
25E04



M 1. i 'II ',,!,.
F mission Vapoi
FJaN'Flisp Fartoi
(g/sect(ug/m'i g/s
1 23F 03 38
271E05 38
8 IE 05 38
5 44E 05 38
2 68E 06 38
7 95E 05 38
6 75E 04 38
1 72E 08 3«
2 23E 05 38
2 83E 05 3 8


May Oft Site
Emission Vapoi
RateDisp Factor
(g/sec)(ug/m3 g/s
1 IDE 03 29868
2 44E 05 298 68
7 3E 05 298 68
4 90E 05 298 68
241E06 29868
7 16E 05 29868
6 08E 04 298 98
1 55E 06 298 68
201E05 29868
2 55E 05 208 68


Ma. no s-te
Fm.ssion Vapor
RateDisp Factor
Ig/spc)(ug(rn3 g/s
541E05 2031
1 19E 06 203 t
3 6E 06 203 1
2 40E 06 203 1
1 18E 07 203 1
351E06 2031
2 98E 05 203 1
7 58E 08 203 1
9 86E 07 203 1
1 25E 06 203 1


Max OH S/!e
Emission Vapor
RaleDisp Factor
(g/sec)(ug/m3 • g/s
1 16E 02 679
257E04 679
7 7E 04 67 9
5 16E 04 67 g
254E05 679
754E04 67 g
6 40E 03 679
1 63E 05 679
212E04 679
263E04 6? 9



Ma,
i '11 Sttp
Cone
(uq/m1|
00047
00001
00003
0 0002
00000
0 0003
00026
00000
00001
00001


Max
OH Sile
Cone
(ug/m3]
03285
00073
00218
00146
00007
00214
0 1818
00005
00060
0 0076


OH Slip
Cone
lug/ml)
0 0110
00002
00007
00005
00000
00007
00061
00000
00002
00003


Max
OH Slip
Cone
0 1969
00044
00130
00088
OOOQJ
00128
0 1086
00003
00036
00045



1 IMCPi
Adult
F >posuip
(mq/kq d)
1 6E 07
36E 09
1 IF 08
7 3F 09
36E 10
1 IE 08
90E 08
2 3F 10
30E 09
38F 09


Cancer
Adult
Exposure
(mg/kg d)
1 2F 05
26E 07
7 7C 07
52E 07
2 5F 08
7 5F 07
6 4E 06
1 6E 08
2 1E 07
2 7E 07


Canc-r
Adult
Exposure
(mg/kg d)
39E 07
85E 09
26E 08
1 7E 08
84E 10
25E 08
2 1E 07
54E 10
7 1EOB
89E 09


Cancer
Adult
Exposure
(mg/kg d)
69E 06
1 5F 07
4 6F 07
3 IE 07
1 5t 08
4 5E 07
3 8F. 06
9 7E 09
1 3E 07
1 6F 07



Cancel Cam pr
(. hild School age
Exposure Exposure
(mq/kq d) (mg/kg d)
4 IE 07 25F 07
9 OE 09 5 5E 09
2 7E 08 1 6E 08
1 BE 08 1 1E 08
8 9E 10 5 4E 10
2 6E 08 1 6E 08
2 2E 07 1 4E 07
5 7E 10 3 5E 10
7 "IE 09 4 5E 09
9 4F 09 5 7E 09


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
2 9E OS 1 7E 05
64E07 39E07
1 9E 06 1 2E 06
1 3E 06 7 8E 07
6 3E 08 3 8E 08
1 9E 06 1 IE 06
1 6E 05 9 6E 06
4 1E 08 25E 08
53E07 32E07
6 7F 07 4 OF 07


Cancer Cancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
96E07 58E07
2 1E 08 1 3E 08
6 4E 08 3 9E 08
4 3E 08 2 6E 08
2 1E 09 1 3E 09
6 3E 08 3 8E 08
5 3E 07 3 2E 07
1 4E 09 8 2E 10
1 BE 08 1 IE 08
2 2E 08 1 3E 08


Cancer Cancel
Child School age
Exposure Exposure
(mg/kg d) {mg/kg d}
1 7E 05 1 OE 05
38E 07 2 3E 07
1 1E 06 6 QF 07
7 7E 0? 4 6F 07
3 BE 06 2 3E 08
1 1E 06 68F 07
9 5E 06 5 8E 06
2 4E 08 1 5E 08
32E 07 1 9F 07
4 OF 07 2 4F 07



Nonranrei
Adult
t xposuip
(mq/kq d)
1 3E 06
2 BE 08
8 4E 08
5 7E 08
2 BF 09
8 3F 08
70E 07
1 8E 09
23F 08
29F 08


Noncancer
Adult
Exposure
(mg/kg d)
90E 05
20E06
60E 06
40E 06
20E 07
59E 06
50E 05
1 3E 07
1 6E 06
2 IF 06


IJnncancer
Adult
Exposure
(mg/kg d)
30E 06
66E 08
20E 07
1 3E 07
66E 09
20E 07
1 7E 06
42E09
55E08
70E 08


Noncancer
Adull
Exposure
(mg/kg d)
5 4F 05
1 2t 06
3 6E 06
2 4E 06
1 2E 07
3 5E 06
30E 05
76E 09
99F 07
1 2F 06



Noncancer Noncancer
Child School agp
Exposure Exposure
(mg/kg d) (mg/kg d(
4 8E 06 2 9E 06
1 1E 07 64E 08
3 1C 07 1 9E 07
21E07 1 3E 07
1 OE 08 6 3E 09
3 IE 07 1 9E07
2 6E 06 1 6E 06
6 7E 09 4 OE 09
8 7E 08 5 2E 08
1 1E 07 6 7E 08


Noncancer Noncdncef
Child School-age
Exposure Exposure
(mg/kg d) (mg/kg d)
3 4E 04 2 OE 04
7 5E 06 4 5E 08
2 2E 05 1 3E 05
1 5E 05 9 1E 06
7 4E 07 4 5E 07
2 2E 05 1 3E 05
1 9E 04 1 IE 04
4 7E 07 2 96 07
6 1E 06 3 7E 06
7 8E 08 4 7E 06


Noncancer Noncancer
Child School-age
Exposure Exposure
(mg/kg d) (mg/kg-d)
1 1E05 6 BE 06
2 5E 07 1 5E 07
7 4E 07 4 5E 07
5 OE 07 3 OE 07
2 5E 08 1 5E 08
7 3E 07 4 4E 07
6 2E 06 3 7E 08
1 6E 08 9 5E 09
2 OE 07 1 2E 07
26E07 1 BE 07


Noncancer Noncancer
Child School age
Exposure Exposure
(mg/kg d) (mg/kg d)
2 OE 04 1 2E 04
4 5F 06 2 7F 06
1 If 05 8 IT 06
9 OF 06 5 4F 06
4 4E 07 2 7F 07
1 3E 05 7 9F 06
1 1E 04 6 7E 05
28E 07 1 7E 07
3 7E 06 2 2E 06
4 7F 06 2 IF 06



CAB
Adult
Cancer
Risk
0
9F 10
0
4E 10
3E 10
IE 09
4E09
4E 09
3E 08
0

39E-OB
WWTank
Adull
Cancer
Risk
0
6E-08
0
3E08
2E08
7E08
3E07
3E07
2E-08
0

27E-06
Truck
Adult
Cancer
Risk
0
2F 09
0
9E 10
BE 10
2E09
1E08
9E09
7E08
0

9 1E-08
Tank Farm
Adult
Cancer
Risk
0
4F 08
Q
2F OH
1F 08
4F OH
21 07
2E 07
1 1 06


1 ?F OS
CAB CAB
Child School agp
Cancpi Cancpr
Risk Risk
0 0
2F 09 IF 09
0 0
1E 09 6E 10
7E 10 4E 10
2E09 1E09
1E 08 6E 09
IE 08 6E 09
7F 08 4E-08
0 0

9 6E-08 9 8E-08
WW Tank WW Tank
Child School age
Cancel Cancer
Risk Risk
0 0
2E-07 9F 08
0 0
7E08 4E-08
5E-08 3E 08
2E 07 1E 07
7E-07 4E 07
7E 07 4E 07
5E 06 3F 06
0 0

6BE-O6 4 1E-OS
Truck Truck
Child School-age
Cancer Cancer
Risk Rrsk
0 0
5E 09 3E 09
0 0
2E 09 IE 09
2E 09 1E-09
6E 09 3E 09
2E08 IE 08
2E 08 IE 08
2E-07 1E 07
0 0

23E-07 1 4E-07
Tank F arm lank Farm
Child School agp
Risk Risk
0 0
IF 08 TF 08
0 0
4E 08 21 tm
3! OB 21 08
11 07 r,| OB
4F 07 IF 07
4( 07 21 07
3F or, .)( of,
0

4 1 F 0^ ? "if Of,
CAB
Adull
Noncancer
MQ
5E05
2E04
IE 04
4E 04
2E 04
2E06
1E-05
ERR
2E05
1E 04
9E05
1 2E-03
WWTank
Adult
Noncancei
HQ
4E 03
IE 02
8E 03
3E02
1E02
2E04
1E03
ERR
1E03
8E03
BE 03
85E-02
Truck
Adult
Noncancei
HQ
IE 04
5E04
3E04
OE04
5E 04
5E08
3E05
ERR
4E05
3E04
2E04
28E-03
Tank Farm
Adult
MO
2F 03
81 01
5f 03
2F 02
flf 0)
11 04
F I'K
7F 04
'.f '1 1
41 ri ;
•5 IF 0?
CAR
Child
Moncancer
MQ
2E04
7E 04
4E 04
1E 03
7E04
9E06
5E05
ERR
BEOS
4E04
3E04
4 5E-03
WW Tank
Child
Noncancer
HQ
1E02
5E02
3E02
1E01
5E02
6E 04
4E03
ERR
4E03
3E02
2E02
32E-01
Truck
Child
Noncancer
HQ
4E 04
2E 03
IE 03
3E03
2E03
2E 05
1E 04
ERR
1F04
1E03
8E 04
1 1E 02
lank larm
Child
HO
61 01
)l 02
21 02
11 02
11 ')4
'1 0!
1 I'l?
'.! 03
/( '!/
11 02
t IF ni
CAB
School ncjf
Nonrancei
MO
IE 04
4E 04
3E 04
9E 04
4E-04
5E06
3E05
ERR
4E 05
3E 04
2E 04
27E-03
WWTank
School age
Noncancer
HQ
8E03
3E02
2E 02
6E02
3E02
4E04
2E-03
ERR
3E03
2E02
1E 02
1 9E-01
Truck
School age
Noncancei
HO
3E 04
1E01
6E04
2E03
1E 03
1E 05
7F 05
FRR
9E05
6E 04
5E04
6 4F-03
Link 1 arm
School age
HO
'.(" 03
21 02
11 02
4F 02
?( 02
2F 04
1! 03
F I«U
2F 03
If 02
"1 r,.
t ir ni
> V  Append'* V TO
-------
EAST SECTOR
ASH HANDLING
i hrmicai
Arspnic
Rariurn
Cadmium
ead
Nickel
Selprnum
Silver
Total Cyanide
Total RIsK/HI
WEST SECTOR
ASH HANDLING

Chpmic.il
Arsenic
barium
Cadmium
ead
Jickpl
Selenium
Silver
I ol.il Cyanide
Total Risk/Hi
IORTH SECTOR
iSH HANDLING

hpmicat
isenic
anum
admium
ead
ickel
elenium
ilver
ital Cyanide
i 3tal Risk/Hi
DUTH SECTOR
5H HANDLING

ipmi'-al
\ senir
ruim
iilrmum
id
kpl
1 ipniurn
pr
)! Cvjnulp
tal Rrsk/HI
. .lull
M,,,,,,
f rl' t"l
(niq'kq d) 1
51)
NA
6 1
NA
(184
NA
NA
NA

Inhal
Slope
Factor
(mg/kg d) 1
50
HA
6 1
NA
084
tIA
NA
NA

lrih.il
SlM(lP
( ,V.I'II
(itiq'kg ill 1
51)
HA
6 1
HA
084
HA
HA
HA

Inhal
Slope
Factor
(mg/kg d) 1
50
NA
6 1
NA
n 8-1
HA
HA
NA


RAC

n ?63
0 125
0 438
HA
17 5
4 375
4 375
17 5



RAC
(ug/m3)
0263
0 125
0438
NA
17 5
4 375
4375
17 5



RAC
lug/ml)
om
0 125
0 438
HA
17 5
4 375
4 375
17 5



RAC
(ug/m3)
0 263
0 125
0 438
NA
17 5
4 375
4 375
17 6


Inhal ill in
PtO
|mq/kq d)
7 51 n')
3 6E 05
1 3F 04
0 OE ' 00
50E 03
1 3E 03
1 3E 03
5 OF 03


Inhalation
RfD
(mg/Kg d)
75E 05
36E 05
1 3E 04
0 OE'OO
50E 03
1 3E 03
1 3E 03
5 OF 03


Inh.V lli in
If HI
(mg/kg ill
7 5E (ft
3 6F 05
1 3f 04
0 OE'OO
50E 03
1 3E-03
1 3E 03
5 OE 03


Inhalation
RfD
(mg/kg d)
75E05
36E 05
1 3E 04
0 OE • 00
50E 03
1 3E 03
1 3E 03
5 OE 03

A.q ( !>,!
! mi, sum ('.tit" ul, ilp
(ql'rc'wnn 4q,
1 37E 06 7 96
6 75E 07 7 96
2 86E 05 7 96
1 45E 05 7 96
2 92E 07 7 96
8 23E 08 7 96
1 04E 07 ' 7 96
1 41F 07 7 96

Avg West
Emission Participate
Rale DF
(g/sec)(ug/m3 4q/
1 37E 06 9 54
6 75E 07 954
2 86E 05 9 54
1 45E 05 9 54
2 92E 07 9 54
8 23f 08 9 54
1 04F 07 954
1 41! (17 0 «,.)

Avg I). .Mli
FmisS'un fait" mate
Rale (T
tfj'spr||,Kj/mt 4<,/
1 37f 06 5 '4
6 75F 07 5 '4
2 Bf F 05 5 74
1 45F U'> ', 74
2 92E 07 5 7.1
823E08 574
1 04E 07 5 74
14IE07 574

Avg South
Emission Paniculate
Rale DF
(g/sec)(ug/m3 4q/
1 37E 06 58
6 75E 07 58
2 86E 05 58
1 45E 05 58
292EO? 58
823E03 58
1 04E 07 5 B
1 41E 07 5 H

Avg
OH Slip
(uq/ml)
2 7F 06
1 3F 06
5 7E 05
2 9F 05
5 BF 07
t 6E 07
2 1E 07
2 BF 07

Avg
OtT Site
Cone
(ug/m3)
33E06
1 6F 06
6 BE 05
35E 05
7 OF 07
2 (it 07
25( 07
3 4F 07

Avg
Off Slip
( one
(uq'ml)
2 Of. 1)6
9 7E 1)7
4 If 1)5
2 If 05
4 2f 07
1 2( 07
1 5F 07
2 OF 07

Avg
on Sitp
Cone
(ug/m3)
2 OE 06
9 8E 07
4 1E 05
2 1F 05
4 2F 07
1 2C 07
1 cit 1)7
2 or 0?

C ,inc or
Adult
(mq/kq d)
9 r,l 11
47! 11
2 OF 09
1 (IF 09
2 OF It
5BF 12
7 3F 12
9 OF 12

Cancpr
Adult
Exposure
(mg/kg d)
1 2E 10
5 7E 11
2 4E 09
1 2E 09
2 5t 11
69E. 12
8 7F 12
1 2F 11

Cancer
Adult
Exposure
(mg/kq d)
69E 11
34E 11
t 4E 09
7 3E 10
1 5E 1 1
42E 12
53F 12
7 1F 12

Cancer
Arlult
Exposure
(mg/kq d)
7 OE 11
3 4F 11
1 5E 09
7 4F 10
1 Sf 11
4 2F 12
53F 12
7 2F 12

<" ciiu.pi Canrpr Noncancci Noru.atu-Pi Noncancpi f
Child Si.hniil ,icjp Adult Child School agp
(inq/kq d) fmrj'kq d) (mq/kq d) (mq/kg d) (tng/kq d)
2 4F 10 1 4t 11) 7 5E 10 2 BE 09 1 7E 09
1 ?E 10 71F11 3 7E 10 t 4E 09 8 3E 10
5 OF 09 3 OE 09 t 6E 08 5 8E 08 3 5E 08
2 5F 09 1 5E 09 7 9E 09 3 OE 08 1 8E 08
51E11 31E11 1 OE 10 59E10 36E-10
1 4E 11 8 7E 12 4 5E 11 1 7E 10 1 OE 10
1 8E 11 1 IE 11 5 7E 11 2 IE 10 1 3E 10
25F 11 t If 11 7 7F 11 29E 10 1 7E 10

il.il Hoith
Adult
Risk
5F 09
OE'OO
1E 08
OE'OO
2E 11
OE'OO
OE'OQ
OE'OO
1 7E-08
Cancer Cancer Noncancer Noncancer Noncancer Total North
Child School-age Adult Child School age
Exposure Exposure Exposure Exposure Exposure
(mg/kg d) (mg/kg d) (mg/kg d) (mg/kg-d) (mg/kg-d)
29E10 1 7E 10 89E10 3 3E 09 2 OE-09
1 4E 10 85E11 44E10 1 6E 09 1 OE-09
6 OE 09 3 6E 09 1 9E 08 7 OE-08 4 2E-08
3 OF 09 1 BE 09 9 5E 09 3 5E 08 2 1E-08
6 IE 11 37F11 1 9E 10 7 1E 10 4 3E-10
1 7F 11 IDF 11 54E11 20E10 1 2E 10
22E11 13F11 6 BE 11 2 5E 10 t 5E-10
29E11 IRFtl 92E-11 .3 4E 10 2 1E-10

Adult
Cancer
Risk
6E09
OE'OO
IF 08
OE'OO
2E 11
OE'OO
DE'OO
OE'OO
2 OE-08
Cancer C aor,er Noncancer Noncancer Noncancer Total North
Child School age Adult Child School age
Exposure Exposure Exposure Exposure Exposure
(mq/kq d) (mq/kg d) (mg/kg d) (mg/kg-d) (mg/kg d)
1 7E 10 1 OE 1" 5 4E 10 2 OE 09 1 2E 09
85E11 51F11 27E1D 9 9E 10 6 OE 10
36E09 2 2E 09 1 IE 08 4 2E 08 2 5E 08
1 8F 09 1 IE 09 5 7E 09 2 IE 08 1 3E 08
37E11 22E11 1 1E 10 4 3E 10 26E-10
10E11 63E12 32E11 1 2E 10 73E-11
13E11 79E12 4 1E-11 1 5E 10 92E-11
1RF11 1 1E-11 55E-11 2 1E-10 1 3E-10

Adult
Cancel
Risk
3E 09
OE'OO
9E09
OE'OO
1E-11
OE'OO
OE'OO
OE'OO
12E-C8
Cancer Cancel Noncancer Noncancer Noncancer Total North
Child School age Adult Child School age
Exposure Exposure Exposure Exposure Exposure
(mg/kq d) (mg/kg d) (mg/kg-d) (mg/kg d) (mg/kg d)
1 7E 10 1 1E 10 54E10 2 OE 09 t 2E 09
86E11 52E11 2 7E 10 1 OE 09 6 1E 10
36E09 ? ?F 09 1 1F 08 4 ?E 08 2 6E 08
1 8F. 03 1 1F 09 58F09 7 2F 08 1 IF OR
37E11 22E11 1 2F 10 4 3H 10 7 or 10
1 HF 11 6 if 12 3 M 11 1 ?E 10 7 4F 11
1 )F 11 8 i'f. 12 4 IF 11 1 5F 10 ') It 11
1 H! 1 1 11111 5 r,F 1 1 ) If 10 1 11 in

Adult
Cancer
Risk
3F 09
OE'OO
9F 09
(IF'(K)
1f 11
Dt '00
1)1 •( 10
'II '(jrj
1 ?E-OS
Iot.lt North lotnl Ninth
( luld School aqi-
Risk - Risk
1F (18 7F 09
OF '00 OE'OO
3E 08 2F 08
OE'OO OE'OO
4F 11 3F 11
OE'OO OE'OO
OE'OO OE'OO
OF. '00 OE'OO
4 2E-OB 2.6E-OB
nt.il Ninth Inl it Ninth liil.it Ninth
Adult
HO
IE 05
IE 05
IE 04
ERR
3E 08
4E08
5E08
2E08
1.4E-04
(JiiM School nqp
limit .inrpl NmiratHPI
HO HO
4F 05 ?! 05
4F 05 2F 05
IE 04 3| (14
FRR ERR
IE 07 7F 08
IE 07 BF 08
2E07 1E CI7
6E 08 3C 08
5 4E-04 3 3E-04
Total North Total North Total North Total North Total North
Child School-age
Cancer Cancpr
Risk Risk
1F 08 9E 09
HE '00 OE'OO
4E 08 2E 06
OE'OO OE'OO
5F 11 3E 11
OE'OO OE'OO
OE'OO OE'OO
OE'OO OE'OO
S1E-08 3.16-08
Total North Total North
Child School age
Cancer Cancel
Risk Risk
9F-09 5E 09
OE'OO OE'OO
2E: 08 1E 08
OE'OO OE'OO
3E 1 1 2E 1 1
OE'OO OE'OO
OE'OO OE'OO
OE'OO OE'OO
31E-08 1.8E-08
Total North Total North
Child School agp
C.incer Cancpr
Risk Risk
9F 09 5F 09
OF '00 OE'OO
2F 08 1F Of!
D( '00 OF' 00
if 11 7F 11
Of 'DO 1)1 >l)l)
ill •(«) ni inn
MI -(in ni M)n
3 1E-08 1 9E-OR
Adult
Noncancer
HO
1E05
IE 05
1E04
ERR
IE 08
IE 08
5E 08
2EOB
1.7E-04
Total North
Adult
Noncancei
HO
7E 06
7E 06
9E05
ERR
2E08
3E08
3E08
1E08
1.0E-04
Total North
Adult
Nonr anr,pr
HO
7f 06
RI on
It (\r,
f Rl*
7! Ml!
tl Oil
If Of)
11 O'l
1 1E-04
Child School age
Noncancer Nonrancer
HO I IO
4E 05 3E 05
5E-05 3C 05
RE -04 IF 04
ERR ERR
1E 07 9F 08
2E 07 1C 07
2E 07 IF 07
7E 08 4E 08
6 5E-04 3 9E-04
Total North Total North
Child School aqp
Noncancei t loncancpr
HO HO
3F 05 2F 05
3E 05 2F 05
3E 04 2[ 04
ERR ERR
9E 08 5E 08
IE 07 6E 08
IE 07 7F 08
4f£ Of! 3E OB
3 9E-04 2 4E-04
lol.il North Total North
Chili) School agp
Nonrancpr Nonrancpr
HO HO
3t 05 7f 05
« 01 2f 115
M 04 ?f 1)4
1 PR ! I'R
')! Hit 51 OB
11 07 r,[ ni]
If (If 71 <«
41 O'i )[ DM
3 9E-04 2 4E 04
-------
ASH HANDLING lnh.il
MAX INHALATION Slope

Chemical
Arsenic
Barium
Cadmium
1 end
Nickel
Selenium
Silver
I Dial Cyanide
Total Risk/Hi
f actor
(mq/kq d) 1
50
tIA
6 1
NA
084
NA
NA
HA

RAG
(uq/m3)
o 263
0 125
0 438
MA
17 5
4375
4 3T5
17 5

Inhalation
RID
(mg/kg d)
7 5E 05
3 GE 05
1 3E 04
0 OE'OO
50E 03
1 3E 03
1 3E 03
50E 03

Max (311 Sil
Emission Participate
RatePisp F ado
(q/spcl(nq/m3
t 37E 06
6 75E 07
2 86 E 05
1 45E 05
292E 07
8 23E 08
1 04E 07
t 41F 07

9's
64
04
64
64
64
64
64
r>4

Max
Off Site
Cone
(ug/m3)
8 Bb 05
4 3C 05
1 BE 0)
93E 04
1 9E 05
53E 06
6 7E 06
9 OF 06

C anrnr
Adull
F xposiite
(niq/kq dl
3 IE 09
1 r;F 09
64F 08
3 3E Ofl
66E 10
1 9E 10
1 3E 10
3 2F 10

Cancer Cancel
Child School age
Exposure
(mq/kq d)
7 7! 09
3 8F 09
1 HE 07
B 1F 08
1 6F 09
4 6E 10
58E 10
7 9F 10

Exposure
(mq/kq d)
4 GF 09
2 3F 09
9 7E 08
4 9E 08
9 9E 10
2 BE 10
35E 10
4 8F 10

Noncancer
Adult
Exposure
(iriq/kq d)
2 4F 08
1 ?E 08
5 OE 07
2 5F 07
5 1E 09
1 4E 09
1 8E 09
2 5F 09

Noncancer NoncancerAsh HaruJlinAsh HandlinAsh HandhrxAsh HaniJlrnAsh HandlinAsh tlaiullin
Child School aqe Adull Child School age Adult Child S< hool age
Exposure
(mg/kq d)
90E 08
4 4E 08
1 9E 06
95E07
1 9E 08
54E 09
68E09
92E 09

Exposure
(mg/kq d)
5 4E 08
2 7E 08
1 1E 06
5 7E 07
1 2E 08
3 3E 09
4 1E09
5 6E 09

Cancer
Risk
2F 07
OE'OO
4F 07
OE'OO
6E 10
OE'OO
OE'dO
OE'OO
5E-07
Cancer
Risk
4F 07
OE'OO
1E 06
01: ' 00
1F 09
OE'OO
OE'OO
OE'OO
1E-06
Cancer Nnnrancer N
Risk
2E 07
OE'OO
6E 07
OE'OO
8E 10
OE'OO
OE'OO
OE'OO
8E-07
HO
3E 04
3E 04
4E 03
ERR
1E 06
1E 06
1E 06
5E 07
5E-03
oncincei Uoru anrer
HO
1E 03
1E 03
1E-02
ERR
4F 06
4E 06
5E 06
2E 06
2E-02
MQ
7E 04
7f 04
9E 03
f RR
2E 06
3E 06
31. 06
1E OG
1E-02
-------
                       ( im u PF^.'Uf NI
                       typ.r ,l) ( am Pi n>,lr«i
                        ag r«pos    39 p"1'
               Suba'f a   vrg mq    vrg mg
                                                          Ini.l ,,,g
TAST
Arsenic
Barium
Cadmium
NicVel
Selenium
Sirvef
Cyan.de
NORTH
Arsenic
Barium
Cadmium
Nickel
Selenium
Sttve*
! Cyanide
SOUTH
Arsenic
3a,Mm
ladmium
-' Nickel
Selenium
1 jifvei
J >amde
", VEST
krsenic
lanum
! -admium
lick el
.elentum
>ltv«l
ya.ide

East
Easl
Fasl
East
East
Easl
East

North
North
North
North
North
North
North

South
South
South
South
South
South
Soulh

Wes
Wes
Wes
Wes
Wes
Wet
Wes

2 IE 12
OOE'OO
OOF'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 7E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 1E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

t 9E 12
OOE'OO
OOE'OO
OOE '00
OOE'OO
OOE'OO
ERR

5 if 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

4 4E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE»00
ERR

2 7E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

5 IE 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 8F 1?
OOE'OO
OOF'OO
OOE'OO
OOE'OO
OOE '00
ERR

1 SE 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

92E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 7E 12
OOE'OO
OOE'OO
OOE'OO
OOF'OO
OOE'OO
ERR

4 Of 16
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOf '00
ERR

32E 18
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

20E 18
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

38E 18
OOF'OO
OOE -00
OOE -00
OOE -00
OOE'OO
FRR

J5E 12
OOE'OO
OOF'OO
OOE'OO
OOE'OO
OOE'OO
ERR

20E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 3E 12
OOE'OO
OOE'OO
OOE'OO
OOF'OO
OOE'OO
FRR

2 3E 12
OOE'OO
OOE -00
OOE'OO
OOE'OO
OOE'OO
ERR

1 OF 12
OOE '00
OOE'OO
OOF'OO
OOE -00
OOE'OO
f RR

t SE 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

94E 13
OOE'OO
OOE'OO
OOE'OO
OOE '00
OOE'OO
ERR

1 BE 12
OOF'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

) «F 11
0 OF • (X)
OOF -00
0 OE • 00
OOF'OO
0 01 • Oil
frm

28E 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 7E 11
OOE'OO
OOE'OO
OOE'OO
OOF'OO
OOE'OO
ERR

3 2E 11
OOE'OO
OOF'OO
OOE '00
OOE'OO
OOE'OO
ERR

flfiF M
001 '00
0 OF • (X)
001 -00
0 Of • 00
OOF •(«)
ERR

5 3F 13
OOE'OO
OOE'OO
OOF'OO
OOE'OO
OOE'OO
FRR

3 3F 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

8 2E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

J II 11
ool -oo
0 01 '(X)
out -uo
0 Of • 00
0 OF • 00
FRR

3SE 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

22E 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

4 IE 11
OOE'OO
OOE -00
OOf'OO
OOE'OO
OOE'OO
FRR
I MAXIMUM LOCATION
.rsemc
larium
admium
lH.K«l
elentum
llvni
ranida
Ma mum
Ma mum
Ma mum
Ma mum
Ma mum
Ma mum
Max mum
1 2E 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
29E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
1 OE 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
2 2E 15
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR
1 4E 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
t OE 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
1 BE 10
OOF'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
38E 12
OOE'OO
OOE'OO
OOE'OO
DOE '00
OOE'OO
FRR
24E 10
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
( Ul|() HI S
lypif a' lia/.i
ag f "pos
vrq ing
4 nf 08
t « 10
8 If 07
5 ?f 10
34E 10
1 2F 10
( wn
3 7E 08
93E 11
BSE 07
43E 10
2 BE 10
59E 10
FRR
23EOS
58E 11
4 1E 07
2 BE 10
1 7E 10
3 BE 10
ERR
43E08
1 IE 10
7 BE 07
48E tO
32E 10
8 BE 10
ERR
27E07
8 BE 10
4flE08
29E09
1 9E09
40E09
ERR
<(>( til
'd indie PS
ag p. ill
vrg mq
1 ?F OB
41(11
351 0?
36t 10
1 9F 10
49E in
ERR
9 BE 09
33E 11
2 BE 07
29E 10
1 8E 10
40E 10
ERR
80E 09
20E 11
1 7E07
1 8E 10
9 7E 11
25E 10
ERR
1 1E08
39E 11
33E07
34E 10
18E 10
4«E 10
ERR
BSE 08
22E 10
19E06
19E09
10E09
27E09
ERR


lp,ity
vrq ,nq
4 0( 08
1 5t 10
5ftf 07
1 SI 10
1 K 10
6 IF. 10
f RR
33E 08
1 2E 10
4 7E07
1 3E 10
9 7E 11
49E 10
ERR
20E08
75E 11
29E07
79E 11
8 IE 11
3 IE 10
ERR
3 BE 08
1 4E 10
54E07
1 5E 10
1 IE 10
5 BE 10
ERR
23E07
83E 10
32E06
88E 10
see 10
33E09
ERR


root
vrg mq
8BC 12
i sr u
1 3F 09
1 81 11
5 7E 14
1 2F 1?
ERR
7 2E 12
8 IE 14
10E09
1 4E 14
4 BE 14
98E 13
ERR
45E 12
3 BE 14
83E 10
B9E IS
2 BE 14
8 IE 13
ERR
84E 12
7 IE 14
1 2E09
1 7E 14
S4E 14
1 1E 12
FRR
4 BE 11
4 1E 13
8 BE 09
98E 14
3 IE 13
85E 12
ERR


119 enpos
Ililil ing
56F 08
1 4E 10
9 7t 07
8 3E 10
4 1E 10
fl 7£ 10
ERR
45EOB
1 IE 10
79E07
51E 10
33E 10
7 IE 10
ERR
2 BE 08
TOE 11
49E 07
32E 10
2 IE 10
44E 10
ERR
52108
1 3E 10
B IE 07
80E 10
39E 10
82E 10
ERR
32E07
7»E 10
S5E06
35E09
23EOfl
4 BE 09
ERR


ag piot
lluil ing
4 IE 08
1 4E tO
1 2E 08
1 JE 09
8 7E 10
t 7E09
ERR
34EOB
1 IE 10
97E07
1 OE 09
S4E 10
14E09
ERR
2 IE 08
7 1E 11
90E07
82E 10
34E 10
BSE tO
ERR
39E08
1 3E 10
1 IE 08
1 2E09
BSE 10
16E09
ERR
23E07
7 BE 10
BSE 06
87E09
3 BE 09
• 2E09
ERR

'
soil
1114
7 5F 07
48E 10
32E 07
1 BE 09
40E 09
7 BE 10
ERR
8 1E07
39E 10
2 BE 07
1 SE 09
33E09
84E 10
ERR
3 BE 07
24E 10
1 8E 07
91E 10
20E09
39E 10
ERR
7 IE 07
4 BE 10
30E07
1 7E 09
3 BE 09
74E 10
ERR
4 1E 08
2 BE 09
1 7EOfl
9 BE 09
22E 08
42E09
FRR


soil drim
contact
8 7E 14
2 3E 12
79E 14
7 IE 13
99E 14
19E 14
EHH
54E 14
1 9E 12
84E 14
5 BE 13
B IE 14
18E 14
ERR
34E 14
1 2E 12
40E 14
38E 13
SOE 14
B/E tS
ERR
«3E 14
22E 12
75E II
88E 13
94E 14
1 8E 14
FRR
38E 13
1 3E 11
43E 13
39E 12
54E 13
10£ 11
ERR

tntAL
srm VF1
Ml
95E 07
1 IE 09
42E Ofl
4 7E 09
5 BE 09
•S2E09
FRR
7 7E07
8 7E 10
•ME Ofl
3 BE 09
4 7E 09
4 2E09
ERR
4 BE 07
S4E 10
2 lEOfl
24E 09
29E 09
2 BE Ofl
FRR
90E07
1 OE09
40E08
45E09
55E 09
49EM
FRR
S2EOB
S9E09
23E05
2 BE Ofl
3 IE OB
2 BE 08
FRR
OTE
RR  =  Ruki and HOs can not be calculated lor cyanide because chemical «p«i!ic values c»n nol br e
 olume V, Appendix  V-20
8
-------

rhrmic.fl
EAST
Ar^emc
Banum
C admiuni
Nickel
Seitfnium
Silver
Cyanide
NORTH
Auenic
Barium
Cadmium
Nickel
Selenium
Silver
Cyanide
SOUTH
Arsenic
Barium
Cadmium
Nickel
Selenium
Silver
Cyanide
WEST
Anenlc
Barium
Cadmium
Nickel
Selenium
Silver
Cyanide

S*.«

East
East
East
Fasl
Easl
East
East

North
North
North
North
North
North
North

South
South
South
South
South
South
South

Weil
West
Weil
Weil
West
Weil
Weil
S( Ml I' H A
ag r.pos
yen ,ng

1 6F 12
OOE '00
OOE'OO
OOf -00
OOF'OO
OOt '00
FRR

t 3E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

8 1E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 5E 12
OOE'OO
OOF'OO
OOE'OO
OOE'OO
OOE'OO
ERR
';( c MII n
ag p'ol
»*« ">9

4 2E 13
OOE'OO
OOF'OO
OOE'OO
OOE'OO
OOE'OO
FRR

34E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

2 IE 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

40E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

»rg ing

1 4E 12
OOE'OO
OOE'OO
ooe-oo
OOF'OO
OOE'OO
ERR

1 IE 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

BBE 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

t 3E 12
OOE'OO
OOF'OO
OOE'OO
OOE'OO
OOE'OO
ERR

10- il

29f 18
OOF'OO
OOF'OO
OOE'OO
OOf -00
OOF '00
FRR

24E 18
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 SE 18
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

3 BE IB
OOE'OO
ooe-00
OOE'OO
OOE'OO
OOE'OO
ERR

ag f -pos

1 IE 12
OOF '00
OOF '00
OOF'OO
OOF'OO
0 OF ' TO
FRR

1 1E 12
OOF'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

87E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 2E 12
OOE'OO
OOf -00
OOE'OO
OOE'OO
OOE'OO
ERR

ag pinl

9 7F t J
OOF'OO
OOF -00
OOF'OO
OOE '00
OOF'OO
FRR

79? 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

4 BE 13
OOE'OO
OOE '00
OOE'OO
OOE'OO
OOE'OO
ERR

S2E 13
OOE'OO
ooe-00
OOE'OO
OOE'OO
OOE'OO
ERR



4 9f 12
001 -'in
oof • on
oo( -no
oof '00
oor 'no
fRM

40E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

25E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

4 7E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

,„,„.„„

< If 1 1
0 nf • (x)
0 or MX)
0 Of M»)
o of • (X)
nof MO
f RR

3 5F 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

22E 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

4 1E 13
OOE'OO
OOt'OO
OOE'OO
OOE'OO
OOE'OO
ERR

RISK

1 If 1 t
0 i| MX)
C "1 •'«)
o u ••»
001 "XJ
OOE •(»)
F RR

B9E 12
OOE'OO
OOE -OO
OOE'OO
OOE'OO
OOE'OO
ERR

58E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 OE 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
MAXIMUM LOCATION
Arsenic
Bailum
Cadmium
Nickel
Selenium
Silver
Cyanide
Maximum
Maximum
Maximum
Maximum
Maximum
Maximum
Maximum
B2E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
23E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
7 7E 12
0 OE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
1 BE 15
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
7 BE 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
53E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
2 7E It
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
24E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
8 1E 11
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR
Si IK II 11 Af'.f f 1(11 0
typii al ha/a>d indices
*g f «po-.
"9 '"»
5 fir on
S 11 11
fl :i o?
401 10
; 6! 10
"i flf in
f RR
29E 08
7 2E 11
50E 07
33E 10
2 IE tO
45E 10
ERR
t BE 08
45E 11
32E 07
JOE 10
1 3E 10
2 BE 10
ERR
33E08
»3E 11
5 BE 07
38E 10
25E 10
S3E 10
ERR
JOE 07
51E 10
3SE08
22E09
1 5E09
3 1E 09
ERR
ag P'ol
•ifq :nq
9 Jf 00
i :( 11
2 'f 07
2sr 10
1 SI 10
161 10
FRR
7 BE 09
2 BE 11
22E 07
23E 10
1 2E 10
3 1E 10
ERR
t 7E09
186 11
1 4E 07
1 4E 10
76E 11
1 9E 10
ERR
89E09
30E 11
28E07
27E 10
1 4E 10
3 BE 10
ERR
5 IE 06
1 7E 10
1 5E 08
15E09
82E 10
21EW
ERR
Ir.lfy
vr<) ,nq
3 or on
1 If 10
4 If 0'
1 2F 10
90t 11
4 5E 10
FRK
24E 08
90E 11
35E07
BSE 11
73E 11
37E 10
ERR
1 5E08
58E It
22E07
5»E 11
45E 11
2 3E-10
ERR
2 BE 08
1 OE 10
40E07
1 1E 10
84E 11
OE 10
ERR
17E07
82E 10
24E08
8«E 10
5 IE 10
2 SEW
ERR
10' )t
*r<) ing
B5F 12
s fir 14
9 ir to
1 If 14
4 2( 14
B9E 11
FRR
53E 12
45E 14
76E 10
1 IE 14
34E 14
73E 13
ERR
33E 12
28E 14
4 7E 10
88E 15
J1E H
45E 13
ERR
82E 12
S3E 14
8 BE 10
1 2E 14
40E 14
BSE 13
ERR
3 BE 11
30E13
S1E09
7 IE 14
23E13
4 BE 12
ERR
ag e*pns
Iruil mg
29F 08
7 4! 11
' 5 1F 07
3 If" 10
22f 10
46E 10
FRR
24E 08
S9E 11
42E07
2 7E 10
1 8E 10
3 7E 10
ERR
1 5E08
37E 11
28E07
1 7E 10
1 IE 10
23E 10
ERR
27E08
89E 11
48E07
31E 10
2 IE 10
43E-10
ERR
1 7E07
42E 10
29E08
1 BE 09
1 2E09
25E09
ERR
ag pfot
fruit ing
2 2E 08
7 IE 11
8 2E 07
64E 10
35E 10
8 BE 10
ERR
18E08
80E 11
51E07
53E 10
2 BE 10
72E 10
ERR
1 1E08
37E 11
3 IE 07
33E 10
1 8E 10
44E 10
ERR
2 IE 08
70E 11
5 BE 07
61E 10
33E10
>4E 10
ERR
12E07
40E 10
34E08
3 SEW
1 BEO«
48E09
ERR
soil
ing
1 1E 07
70E 11
48E 08
2 BE 10
5 BE 10
1 1E 10
ERR
89E08
57E 11
3 BE 08
21E 10
4 BE 10
B2E 11
ERR
55E08
35E 11
23E08
1 3E 10
29E 10
57E-11
ERR
10E07
«7E 11
44E08
25E 10
5 BE 10
1 1E 10
ERR
59E07
38E 10
25E07
1 4E09
32E09
82E 10
ERR
soil drim
contact
44E 14
1 5E 12
5 2E 14
4 7E 13
BSE 14
1 3E 14
ERR
38E 14
1 3E 12
43E 14
39E 13
S4E 14
10E 14
ERR
22E 14
79E 13
28E 14
24E 13
33E 14
8SE IS
ERR
42E 14
1 5E 12
50E 14
45E 13
«3E 14
12E 14
ERR
24E 13
84E 12
2 BE 13
28E 12
3 BE 13
8 BE 14
ERR
TOIAl
SOIL VFi;
Ml
24E 07
45E 10
25E 08
20E09
1 7E 09
2 BE 09
FUR
1 BE 07
37E 10
20E08
1 7E09
1 3E 09
J3E09
ERR
12E07
23E 10
1 3E08
10EOB
84E 10
1 4E09
FRR
2 2E 07
42E 10
24E08
IDEM
1BEOB
27EOB
ERR
1 3E08
2 SEW
1 4EOS
1 IE 08
9 IE W
18EOB
ERR
NOTE
NU(t
ERR = Ri»«« and HQt can not be calculated lor cyanide because chemical ipecilic valuer can not be estimated
\/olume V, Appendix V-20
-------


Chemical
EAST
Aispmc
Banum
Cadmium
Nickel
Selenium
Silver
Cyanide
NORTH
Arsenic
Barium
Cadmium
Nickel
Selenium
Silvw
Cyanide
SOUTH
Arsenic
Banum
Cadmium
Nickel
Selenium
Silnr
Cyanide
WEST
Arsenic
Barium
"admium
Nickel
Selenium
Sitvm
lyanide


Suharea

Fa*
Ex
Eas
Eas
Eas
Eas
Eas

North
North
North
North
North
North
North

South
South
South
Soulh
South
South
South

West
West
Weil
W«it
Aol
Weil
w«st
I.I 	 ' !""
ag r-pos
vrg ing

1 7E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
FRR

1 4E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

BSE 13
OOE'OO
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ERR

1 8E 12
OOE'OO
OOE'OO
OOE'OO
OOE'OO
ooe-oo
ERR
ft (K.I.S
ag p'ol
"9 '"9

4tm
contact
2 BE 14
97E 13
33E 14
30E 13
4 IE 14
80E 15
ERR
23E 14
7 BE 13
27E 14
24E 13
34E 14
88E 15
ERR
1 4E 14
4 BE 13
1 7E 14
1SE 13
2 IE 14
4 IE 15
ERR
28E 14
B3E 13
3 IE 14
2 BE 13
3 BE 14
7 7E 15
ERR
15E 13
53E 12
1 BE 13
18E 12
23E 13
44E 14
ERR
1O1AI
son vrci
Ml
1 1E 07
24E 10
1 4E Ofl
1 OE09
7 7E 10
15E09
ERR
BOE08
20E 10
1 1E 08
82E 10
83E 10
1 2E09
ERR
5 BE 08
1 2E 10
BBE07
5 IE 10
3 BE 10
78E10
FRR
10E07
23E 10
1 3E08
BBS 10
73E 10
14EOB
ERR
82E07
1 4E 09
78E08
55EOB
43E09
82E09
FRR
'cHume V; Appendix V-20
10
-------
                            APPENDIX V-21

            Summary of Input Parameters Used in Uncertainty Analysis
Volume V
\^c*~A:.. 17 "II
-------
                                   APPENDIX V-21
              Summary of Input Parameters Used in Uncertainty Analysis
     Because the uncertainty analysis focuses on the indirect exposure of subsistence farmers
 to 2,3,4,7,8-PeCDFand arsenic, the important fate and transport model components are the
 constituent concentrations in soil, meat, eggs,  milk, and vegetation. In the HHRA. the
 surface water, sediment, fish, and mother's milk model components were not found to be
 significant contributors to exposure for this population subgroup, and thus the input
 parameters associated with these model components are not included in this analysis.
     The ranges of the possible values for the relevant input parameters are summarized in
 Table IX-1 of Chapter DC.  The rationale for the selection of the ranges are discussed below.
 While  ranges are defined based on available data or guidance to the extent possible, scientific
 judgment is  used to estimate conservative ranges where appropriate data or guidance are
 unavailable.  As discussed  in Chapter IX, these ranges are estimated to represent the 95
 percent confidence interval.

 A.   Chemical and Physical Properties

     •   Henry's Law constant (H)
        2.3.4.7.8-PeCDF:  The Henry's Law  constant of 6.2 x 10~6 atm-m3/mol for
        2.3,4,7,8-PeCDF (U.S. EPA 1994a),  which is calculated from the chemical's vapor
        pressure/water solubility (VP/WS)  ratio (Lyman et al.  1990), is used as the most
        likely value of H.   Vapor pressures estimated for PeCDF congeners range from
        2.0xlO~12 to 5.7xlO~i: atm  (U.S.  EPA 1994a), spanning  a factor of about three.
        Only one value is reported  for the water solubility of PeCDFs; however, values for
        other dioxin and furan congeners have ranges spanning about one order of
        magnitude (U.S. EPA  1994a). Therefore,  the Henry's Law constant for 2,3,4,7,8-
        PeCDF is assumed  to be accurate over a factor of approximately 30, from 8.Ox 10"7
        to 2.4X10"5 atm-m3/mol.

        Arsenic:  Arsenic is assumed to  have a Henry's Law constant of zero (i.e.,
        nonvolatile).
Volume V
Annenrliv V-"M
-------
     •  Octanol/water partition coefficient (K0J
        2.3.4.7.8-PeCDF: The only value of log Kw reported by U.S. EPA (1994a) for
        2,3.4.7,8-PeCDF of 6.92 (Sijm et al. 1989), which corresponds to a value for A",,,, of
        8.3X106, is used as the most likely value of log K^..  Values have been reported for
        log K^ for other PeCDF congeners ranging from 6.19 to 6.79 (Sijm et al. 1Q8Q).
        Thus, the range of log K^, values for all PeCDF congeners spans a factor of about
        one, which corresponds to a range of about  an order of magnitude for K^  values.
        Because the value of log K<,w for 2,3,4,7,8-PeCDF is the upper limit of the range of
        values for all PeCDF congeners, the value of K^ for 2,3,4,7,8-PeCDF is
        conservatively estimated to range over two orders of magnitude, ranging from
        4.2xlO5 to 4.2X107 (which corresponds to values of log Kou. ranging from 5.t> to
        7.6).

        Arsenic:  Value not required for modeling.

     •  Organic carbon adsorption coefficient (K^.)
        2.3.4.7.8-PeCDF:  Values for K^- are based on  the following relationship with the
        octanol/water coefficient (Kw) (U.S. EPA 1993, 1994a):
                                logA'oi. = log Km- 0.21                         (V-21-1)

        This regression equation is based on data collected for ten chemicals  by Karickhoff
        et al. (1979), and is recommended  for chemicals with high Kow values. Using the
        range  for log K^ of 5.6 to 7.6.  K^ ranges from 2.5 x 105  to 2.5 x 107 L/kg, with a
        most likely value of 5.1 x 10" L/kg (using log K^ =6.92).

        Arsenic:  Value not required for modeling.

    •   Soil/water distribution coefficient (Kd,)
        2.3.4.7.8-PeCDF:  For organic compounds,  Kds is calculated as follows (U.S. EPA
        1993,  1994a):

                                  A< = (AJ(OCJ                          (V-21-2)

        where OCSO|1 is the fraction of organic carbon in  soil and K^ is calculated  from the
        relationship with Kw given by equation (V-21-1).  Using the range for log K^ of
        5.6  to 7.6 and a range  for OCsoll of 0.010 to  0.016 (USDA SCS 1968.  1974, 1981.
Volume V
Annendiv V-?l
-------
         1982. 1983, 1989). Kds ranges from 2.500 to 4.0 xlO5 L/kg. with a most likeh
         value of 6.6 xlO4 L/kg (using OCsoiI=0.013 and log Kw=6.92).
        Arsenic: The most likely value for Kds for arsenic is 200 L/kg (Baes et al.
        This value of Kds is estimated by Baes et al. (1984) to be uncertain o\er three
        orders of magnitude, which corresponds to a GSD of 5.62.  Assuming this range
        represents the 95 percent confidence interval of a lognormal distribution, the
        geometric mean is estimated to be 45 L/kg, ranging from 1.4 to 1.400 L/kg.

     •  Diffusion coefficient (Da)
        2.3.4.7.8-PeCDF: Measured values for D, are not available for dioxin-like
        compounds.  Therefore, U.S. EPA (1994a) estimates values based  on the square
        root of the ratio of the  molecular weight of each dioxin-like compound and diphenvl.
        a compound for which  Da is available (Thibodeaux 1979).  Using this method, the
        value of D, for 2,3,4,7,8-PeCDF is 0.047 cm2/sec.  Based on professional judgment.
        the uncertainty associated with this approximation is estimated to be a factor of two.
        The value of Da for 2.3,4,7,8-PeCDF is therefore assumed to range from 0.023 and
        0.1 cnr/s.

        Arsenic:  Value not required for modeling.

B.  Emissions and Atmospheric Transport

    •   Emission rate
        2.3.4.7.8-PeCDF:  As discussed in Chapter En  of Volume IE, emission rates can be
        variable depending on the operating conditions and waste feed composition.  Based
        on data collected during the February 1994 trial burn (four test runs)  and the 22
        performance test runs conducted between August 1993 and August  1994, emission
        rates of 2,3,4,7, 8-PeCDF ranged from 9.0X1Q-11 to 1.5xlO~9 g/sec, with a most
        likely  value of 4.7 x 10~10 g/sec.  Because of the wide variety of operating
        conditions used, this range is assumed to be an  adequate characterization of the
        range  of emission rates. The upper limit of this range is multiplied by a correction
        factor ranging  in value  from  1.0 to 1.5 to account for the possible presence of
        brominated compounds, as discussed in Chapter IX.

        Arsenic:  The most likely value for the emission rate of arsenic  is 3.7x 10~5 g/sec
        (Chapter HI of Volume HI).  This  emission rate is estimated to vary over an order

Volume V
Annendix V-^1                             *>
-------
        of magnitude (Appendix EQ-1 of Volume ED). which corresponds to a GSD of 1.78.
        Assuming this range represents the 95 percent confidence interval of a lognorma!
        distribution, the geometric mean is estimated to be 2.7xlO~5 g/sec. ranging from
        8.4xlO~6to 8.4X10'5 g/sec.

        Atmospheric dispersion
        2.3.4.7.8-PeCDF:  Dispersion factors relating emissions from the WTI incinerator
        to ambient concentrations at the receptor site are developed using the dispersion
        model ISC-COMPDEP. A series  of sensitivity tests of the model predictions to a
        range of inputs was performed to assess the response of the model to uncertainties in
        the model input parameters (Chapter V of Volume IV). Based on an analysis of
        these sensitivity tests and the performance of other similar steady-state  Gaussian
        models, it is estimated that the uncertainty of the annual average concentration
        predictions from ISC-COMPDEP is a  factor of four.  Therefore, the dispersion
        factor for  2,3,4,7,8-PeCDF of 0.914  (/xg/m3)/(g/s) at the location of maximum
        vapor intake is assumed to range from 0.23  to 3.66 (jig/m3)/(g/s).

        Arsenic:  The dispersion factor for arsenic is estimated to be  accurate to within a
        factor of four, based on the sensitivity testing of the ISC-COMPDEP model and
        previous evaluation studies with  the ISC and COMPLEX I models (Chapter V  of
        Volume IV).  Therefore, the dispersion factor for arsenic  of 0.0155 (^g/m3)/(g/'s) at
        the location of maximum wet deposition is assumed to  range from 0.0039 to 0.062
        Wet and dry deposition
        2.3.4.7.8-PeCDF:  Deposition factors are developed relating ambient concentrations
        at the  receptor site to the wet and dry deposition fluxes.  The wet deposition factors
        discussed in Chapter II of Volume IV are maximum values.  The actual peak values
        could  range to as low  as one tenth this value.  For reasons discussed in Chapter IV
        of Volume  IV, the wet deposition algorithm is likely to overestimate near-field wet
        removal rates and, therefore, wet deposition fluxes.  This is due to the use of
        scavenging  coefficients that implicitly include the effects  of both below-cloud and in-
        cloud  scavenging, whereas, near the stack, only below-cloud scavenging occurs
        under  most conditions. To estimate an upper limit for this maximum wet deposition
        factor, the uncertainty in the ISC-COMPDEP model (factor of four) is used.
        However, this is considered very conservative because the wet deposition algorithm
        is likely to  have a bias toward overprediction of wet deposition  fluxes in the near
Volume V
Annpnrliv V-'' 1
-------
         field, where the peak deposition is predicted to occur.  For wet deposition, the
         deposition factor for 2,3,4,7,8-PeCDF of 0.0245 (g/m:-yr)/(g/s) is assumed to range
         from 0.00245 to 0.098 (g/nr-yr)/(g/s).
             Dry deposition factors are estimated to be accurate to within a factor of fi\e.  A
         series of sensitivity tests evaluating the sensitivity of the deposition fluxes  to model
         inputs (e.g., particle size distribution, land use assumptions) show variations from
         the base case results that are within this factor.  For dry deposition, the deposition
         factor for 2,3,4,7,8-PeCDF of 0.00515 (g/m2-yr)/(g/s) is assumed to range from
         0.00103 to 0.026 (g/nr-yr)/(g/s).

         Arsenic:  The same uncertainty factors used for 2,3,4,7,8-PeCDF are assumed to be
         applicable for arsenic.  The dry deposition factor for arsenic of 1.2 x 10~4  (g/nr-
         yr)/(g/s) is assumed to be accurate to within a factor of five, ranging from 2.4x 1(T5
         to 6.0xlO~4 (g/m2-yr)/(g/s).  The maximum predicted wet deposition factor for
         arsenic of 0.221 (g/nr-yr)/(g/s) is assumed to range from 0.0221 to 0.884  (g/nr-
         yr)/(g/s).

     •   Vapor/particle  partitioning fraction ()
         2.3.4.7.8-PeCDF:  No specific data for  were  found for 2,3,4,7,8-PeCDF.
         Therefore, using the theoretical  approach of Junge (1977) as recommended by
         Bidleman (1988). the most likely value for A  1994a), which  is used for
         the range for 2,3,4,7,8-PeCDF.

         Arsenic: Arsenic is assumed to exist  entirely in the paniculate phase (i.e.,  0=1.0).

     •   Wind speed (u)
         According to airport wind speed data  used in this risk assessment (Vreeland 1994),
         wind speeds typically range from 1 to  10 m/sec, with a most likely value of 4.1
        m/sec.

     •  Air temperature (T)
        Based on regional soil surveys (USDA SCS 1968, 1974.  1981,  1982.  1983. 1989).
                                                                ^*
        the  air temperature  in the site vicinity typically ranges from 265 to 301 K,  with a
        most likely value of 293 K.
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Annenriiv V-'M
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    •   Viscosity of air (/*„)
        The average temperature at the site is 293 K, which corresponds to an air viscosit\
        of 1.82xlO~4 g/cnr-s (Perry and Green 1984). For temperatures ranging from 265
        to 301 K, the viscosity of air ranges from 1.68xlO~4 to 1.86xlO~4 g/cnr-s.

    •   Density of air (pa)
        The average temperature at the site is 293 K, which corresponds to an air densiu of
        1.20xlO~3 g/cm3 (Perry and Green 1984). For temperatures ranging from 265 to
        301 K. the density of air ranges from 1.18xlO"3 to 1.33 xlO~3 g/cm3.

C.  Soil Concentration

    •   Soil bulk density (BD)
        Based on  regional soil surveys (USDA SCS 1982, 1983, 1989). the site-specific
        value of BD is estimated to be 1.31 g/m3, ranging from 1.10 to 1.55 g/m3.

    •   Fraction organic carbon in soil (OC8oU)
        Based on  regional soil surveys (USDA SCS 1968, 1974, 1981, 1982,  1983. 1989).
        the site-specific value of OCSOI] is estimated to be 0.013. ranging from 0.010 to
        0.016.

    •   Average annual precipitation (P)
        Based on  regional soil surveys (USDA SCS 1968,  1974, 1981, 1982.  1983. 1989).
        the site-specific average annual precipitation  is 95 cm/year, ranging from 87 to 101
        cm/year.

    •   Average annual irrigation  (I)
        The site-specific value of I is estimated to be 28 cm/year (Jarrett 1994).  During a
        normal crop season, the irrigation need for the area could be as low as 11 cm/year.
        an upper limit on the range  for I is estimated to be  40 cm/year (Jarrett 1994).

    •   Average annual runoff (RO)
        The site-specific value for the annual average  surface water runoff is estimated to
        be 25  cm/year (Jarrett 1994).  The annual average surface wajter runoff for  Ohio is
        estimated to range from 12  to 38 cm/year (Geraghty et al. 1973).
Volume V
Aooendix V-21
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         Average annual evapotranspiration (Ev)
         The site-specific average potential evapotranspiration is estimated to be  88 cm -year
         (Reinke 1994).  The average potential evapotranspiration for Ohio ranges from 60 to
         90 cm/year (Geraghty et al. 1973).  Average annual evapotranspiration  is assumed
         to be half of the potential evapotranspiration (U.S. EPA 1993).

         Soil volumetric water content (65)
         Volumetric  water content, estimated as the midpoint between a soil's field capacit)
         and wilting  point, ranges from 0.10 mL/cm3 for very sandy soils to 0.30 mL/cnr  lor
         heavy loam/clay soils (U.S. EPA 1993).  Based on the recommendation of Seiben
         (1994), the  most likely value used in the risk assessment is 0.25
     •  Enrichment ratio (E)
        Enrichment ratios have been assigned values ranging from 1 to 5 for organic matter.
        phosphorus, and other soil-bound constituents of concern (U.S. EPA 1994a.  1^93)
        Based on EPA guidance (U.S. EPA 1994a,  1993), a value of 3 is selected as the
        most likely value in the risk assessment.

     •  Erosivity factor (R)
        Annual values for the rainfall/erosivity index range from < 50 for the arid western
        United States to 300 or 400 for the Southeast (U.S. EPA 1994a,  1993).  A value of
        125, recommended by Moyer (1994), is selected as the most likely value in the risk
        assessment.

     •  Erodability factor (K)
        Based on regional soil surveys (USDA SCS  1982,  1983, 1989), the site-specific
        value of K  is estimated to be 0.34 yr~', ranging from 0.15 to 0.49 yr"1.

     •  Slope length factor (LS)
        LS is a topographic factor that reflects the influence of slope steepness and length of
        the field in  the direction  of erosion, with values ranging from 0.1  for slopes  < 1.0 7r
        and lengths < 100 feet, to  >2.0 for slopes generally > 10% (U.S. EPA 1994a,
        1993).  Based on EPA guidance (U.S. EPA  1994a. 1993). a range of 0.1 to 2.0 is
        assumed for this  analysis, with a most likely value of 0.20.
Volume V
Annendix V-21
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     •  Cover management factor (C)
        The cover management factor reflects how vegetative cover and cropping practices
        influence erosion, and range from 0.1 for areas with dense vegetative cover to a
        maximum of 1.0 for bare soils (U.S. EPA I994a. 1993).  Based on EPA guidance
        (U.S. EPA 1994a, 1993), the most likely value is set at 0.3.  which is recommended
        for rural settings.
                     •to1-
    •   Supporting practice factor (P,)
        The supporting practice factor reflects the use of surface conditioning,  dikes,  or
        other methods to control runoff/ erosion, and has a value of 1.0 when no such
        practices are employed (U.S. EPA 1994a, 1993).  The uncertainty analysis
        conservatively assumes Ps to be constant at 1.0, given a lack  of information
        suggesting that any supporting practices are used in the area.

    •   Soil loss due  to degradation (ksg)
        2..3.4.7.8-PeCpF:  The degradation soil loss constant of 0.0693 yr"1 recommended
        by U.S. EPA (1994a) for 2,3,4,7,8-PeCDF corresponds  to a  degradation half life of
        10 years.  Fries and Paustenbach  (1990) report that half  lives for  TCDD could be as
        long as 20 years.  Therefore, estimating the degradation  half life to be  uncertain  b\
        a factor of 2,  the values of ksg that correspond to half lives of 5 and 20 years are
        0.139 and 0.0347 yr~l. respectively.

        Arsenic:  It is assumed that arsenic does not degrade in soil (i.e..  ksg=0).

    •   Root concentration factor (RCF)
        2.3.4.7.8-PeCDF:  The root concentration factor is calculated from a correlation
        with Kw (U.S. EPA 1993. 1994a), which was developed by Briggs (1982) for
        lipophilic compounds (i.e.. log Kw >2.0):
                             logtfCF = 0.771ogA^-1.52                     (V-21-3)

        Assuming log Kow ranges from 5.6 to 7.6, RCF ranges from  620 to 21,500 L/kg  for
        2,3,4,7,8-PeCDF, with a most likely value of 6,400 L/kg (using log K^ =6.92).
        Arsenic:  The value for RCF of 0.008 L/kg recommended by'U.S. EPA (1994b) is
        used as the most likely value.  Estimating the uncertainty for arsenic to be
        comparable to that of 2.3,4,7.8-PeCDF, the values of RCF are assumed to range
Volume V
Annpnrliv V-'M
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        over a factor of 35. which corresponds to a GSD of 2.43.  Assuming this range
        represents the 95  percent confidence interval of a lognormal distribution, the
        geometric mean is estimated to be 0.005, ranging from 0.0009 to 0.032.

D.  Meat, Eggs, and Milk Concentrations
    The following parameters are required to determine the constituent concentration in beef.
pork, chicken, eggs, and milk.

    •   Soil bioavailability (Bs)
        From studies measuring the oral bioavailability of TCDD in soil in the diet  of rats.
        the bioavailability of soil is reported to range from 0.5 to 0.8 (U.S. EPA 1994a),
        Because no other  data were available for the bioavailability of PeCDF in soil  in the
        diet of cattle, the  same range is adopted in this assessment, with a most likely value
        of 0.65 (U.S. EPA 1994a).
    •   Fraction of beef that is fat
        According to data reported by Pennington (1989), the average fat content of beef
        (including brisket, chuck,  flank,  ground,  ribs, round, shank, short loin, and wedge-
        bone sirloin) is 0.23, ranging from 0.12 to 0.35.
    •   Fraction of milk that is fat
        The most likely value for the fat content of milk is assumed to be 0.02 (U.S. EPA
        1994a). The value of fat^  is assumed to range from 0.002  (skim milk) to 0.037
        (whole milk) (Pennington 1989).
        Fraction of pork that is fat
        According to data reported by Pennington (1989), the average fat content of pork
        (including arm picnic, bacon, boston blade, center loin, center rib,  ham, leg, loin.
        loin blade,  rump, sausage, shank, shoulder, sirloin, spareribs, and top loin) is 0.23,
        ranging from 0.050 to 0.35.

        Fraction of chicken that is fat (fatcbickM))
        According to data reported by Pennington (1989), the average fat content of chicken
        (including light and dark meat) is 0.058, ranging from 0.015 to 0.12.
Volume V
Aooendix V-21
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        Fraction of eggs that is fat
        The most likely value for the fat content of an egg is assumed to be 0.08. based on
        data reported by CalEPA (1993). McKone (1993). and Goldman et al.  (1989)
        Other estimates of fat content have been reponed as  high as 0.11  (Pennineton  l^S^i
        Therefore, assuming 0.11 represents the upper bound, the lower bound is estimated
        to be 0.05.

        Animal tissue bioconcentration factors (BCF)
        2.3.4.7.8-PeCDF:  McLachlan et al.  (1990) reported the only measured value  of
        BCF for 2,3,4,7,8-PeCDF, 3.1, which is used as the most likely value.  Values  are
        reponed for other dioxin-like compounds in beef and milk fat ranging from 0.05 to
        5.7 (U.S. EPA 1994a; McLachlan et al. 1990; Fries and Paustenbach 1990; Jensen
        and Hummel 1982; Jensen et al.  1981; Arstilla et al.  1981; Parker et al.  1980;
        Firestone et al. 1979). with lower chlorinated congeners generally having higher
        values of BCF than higher chlorinated congeners.  Taking this association of
        decreasing bioconcentration ratios with increasing chlorination into consideration.
        the range of BCF values reported for tetra-, penta-, and hexa-chlorinated dioxins and
        furans, from 0.73 to  5.7, is selected to represent the estimated uncertainty in the
        BCF value for 2,3,4,7.8-PeCDF in the fat content of beef, milk, pork, chicken, and
        eggs.

        Arsenic:  Value not required for modeling.

        Animal tissue biotransfer factors (Ba)
        2.3.4.7.8-PeCDF:  Value not required for modeling.

        Arsenic:  Baes et al.  (1984) and Ng (1982) provided  the only available estimates of
        the ingestion-to-beef biotransfer factor for arsenic of  0.002 day/kg, which is used as
        the most likely value for BabMf.  The GSD of the arsenic biotransfer factors is not
        reponed, however, GSDs for other elements range from 1.3 to 3.8. Therefore, the
        GSD of Babeef for arsenic is conservatively estimated  to be 3.8. which corresponds to
        a geometric mean of  8.2 x 10~4 and values for Babecf ranging  from  5.7 x 10"5 to
        0.012.  For milk and other animal tissues, most  likely biotransfer  factors that have
        been reported are 6.0xlO~5 for milk (Baes et al. 1984). 0.0037 for pork. 0.2011 for
        chicken, and 0.2615 for eggs  (Belcher and Travis 1989).   The same GSD is assumed
        for Ba in milk and other animal tissue  groups, resulting in the following geometric
        means and ranges:  GM = 2.5xlO~5 and range =  1.7x 10~6 to 3.6xlO"4 for  milk:
Volume V
Appendix V-21
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         GM =0.0015 and range = 1. 1 x!0~4 to 0.022 for pork:  GM =0.082 and
         range=0.0057 to 1.2 for chicken; and GM=0.11 and range=0.0074 to 1.5 for
         eggs.
        Plant and soil diet fractions of animals (DFpu,
        The diets of beef cattle, dairy cattle, hogs, and chicken consist of various
        proportions of forage,  grain, silage, and soil.
             For beef cattle, reported soil ingestion rates range from 1 to 18% of dr>  matter
        intake,  which  is 1 to 15% of total intake,  with a typical value of 3% (U.S. EPA
        1990a,  Thorton and Abrams 1983). Therefore, forage, grain, and silage compose
        the remaining portion of the diet. Typical diets for beef cattle reportedh consist of
        72% forage, 4%  grain, and 21% silage (U.S. EPA 1990a, Ensminger 1976).
        Generally, soil ingestion is inversely related to the availability of forage (Fries and
        Paustenbach 1990). The higher soil ingestion rates likely occur under poor pasture
        conditions with sparse  vegetation, whereas periods of lush plant growth  are
        associated with low soil intake.  Because beef cattle often subsist on diets that are
        largely  forage (Fries and Paustenbach 1990), the upper limit of the forage diet
        fraction is assumed to be 99%, with a soil diet fraction of 1 %, in which case the
        lower limits of the silage and grain diet fractions would both be 0%. Under poor
        pasture  conditions or for various dietary considerations, the lower limit of the forage
        diet fraction is estimated based on professional judgment to be one third (33%),
        approximately a factor of two  lower than the typical value of 72%, with the soil
        ingestion increasing to  its maximum value of 15%, and the balance of the  diet
        comprised of an increase from the most likely value in either the silage or grain
        fractions (i.e., either 4% grain and 48% silage or 31 % grain and 21 % silage).  The
        higher silage diet  fraction corresponds to  periods of short growing seasons and low
        rainfall; the higher grain diet fraction corresponds to periods of beef cattle fattening
        (Fries and Paustenbach  1990. NRC 1984).  In summary, for beef cattle, the diet
        fractions are assumed to range from 33 to 99%  forage, 1  to 15% soil. 0 to 31 %
        grain, and 0 to 48% silage.
            Dairy cattle generally do not graze to the extent that beef cattle do,  partly
        because high-producing cows are unable to meet their energy requirements when
        pasture  is their main food source (Bath et  al. 1985).  Therefore, a 99% upper bound
        forage diet fraction for dairy cattle is not likely.  Typical  diets for dairy  cattle
                                                                fr*
        reportedly consist of 64% forage, 15% grain, and 19% silage, with the remaining
        2% intake being soil (U.S.  EPA 1990a).  Reported soil ingestion rates range from 1
        to 7% of total intake, with a typical value of 1% for lactating dairy  cows and 4%
Volume V
Annendix V-71
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        for nonlactating cattle (U.S. EPA 1990a. Fries et al. 1982a).  Because of the lou.
        cost of pasture grass and the high nutritive value of grain, it is unlikely that the diets
        of dairy cattle are completely devoid of either roughage or grain (Bath et al. 1985.
        NRC  1978).  Therefore, based on professional judgment, the lower limits of the
        forage and grain diet fractions are estimated to be 30% and 1%. respective!).
        approximately a factor of two lower than the typical values.  For nutritional reasons.
        grain  does not generally exceed 50% of the total diet (Stallings  1995).  The
        maximum forage diet fraction is estimated to be  92% by assuming  all other diet
        components are at their minimum values.  The maximum silage diet fraction is
        estimated to be 56% by assuming forage and grain are  at their minimum values and
        soil is at its maximum value  (assuming soil and forage  ingestion are inverse!)
        related).  In summary, for dairy cattle, the diet fractions are assumed to range  from
        30 to  92% forage,  1 to 7% soil, 7 to 50% grain, and 0 to 56%  silage.
            Hogs and poultry are not grazing animals, and are assumed not to eat forage.
        Reported soil ingestion rates  for hogs range from 2  to 7% of total intake (U.S. EPA
        1993, Fries and Paustenbach 1990,  Fries et al. 1982b).  Grain reportedly comprises
        35 to  80% of the dry matter  intake  (NRC 1988). with a typical  value of 70% (U.S.
        EPA 1993).  For a soil diet fraction of 2%, the grain diet fraction  is assumed to
        range from 34 to 78%, and the silage diet fraction from 20 to 64%: for a soil diet
        fraction of 7%, the  grain diet fraction is assumed to range from 33 to 75%. and the
        silage diet fraction from  18 to 60%. In summary, for hogs, the diet fractions are
        assumed to range from 2 to 7% soil, 33 to 78%  grain,  and 18 to 64% silage.
            Poultry typically subsist entirely on grain, although free ranging chicken may
        also ingest soil.  For free ranging chicken,  the maximum soil  diet fraction is
        estimated to be 3% of total intake (U.S. EPA  1993), with the remainder of the diet
        comprised of  grain.  Therefore, for chicken, the diet fractions are assumed to range
        from 0 to 3% for soil and  from 97  to 100% for grain.

E.  Vegetation Concentrations
    The following parameters are required to determine the constituent concentration in fruit
and vegetables.

    •   Fraction of wet deposition that adheres to plant surfaces (Fw)
        For organic compounds, the fraction of material  retained on vegetation from wet
        deposition is estimated based on the measurements of Hoffman et al. (1992) of
        particles to three plant types  during moderate and high  intensity rainfall to range
        from 0.32 to 0.79,  with an average of 0.60 (U.S. EPA 1995b).   Based on the

Volume V
Appendix V-?1                            •-          	.  	  ...  .. 	
-------
        measurements of Hoffman et al. (1992) for beryllium. Fw is estimated to range from
        0.32 to 0.60. with an average of 0.46.

        Length of plant's exposure to  deposition (Tp-,)
        The Pennsylvania Agricultural Statistics Service (1994) reponed the following ranges
        for plant exposure to deposition:  0.123 to 0.329 years for exposed vegetables:
        0.247 to 0.329 years for leafy vegetables; 0.096 to 0.150 years for gram; and 0.27
        to 0.36 years for forage. For silage, the range is estimated  to be 0.042 to 0. 122
        years.  Typical values are reported in Table IX- 1.

        Yield or standing crop biomass (Yp,)
        The following ranges for site-specific crop yields are reported in the 1992 Census of
        Agriculture (USDC 1993a,b,c):  0.17 to 0.66 kg DW/nr for grain; 0.29 to 0.57 kg
        DW/nr for forage; and 2.5 to 3.4 kg DW/m2.  For crops for which site-specific
        data are not reported,  the default ranges reported by Belcher and Travis (1989) are
        used:  0.01 to 0.25 kg DW/nr for above ground exposed fruits and vegetables, and
        0.09 to 0.35 kg DW/nr for leafy vegetables. Typical values are reported in Table
        IX- 1.

        Environmental half-life on plant surfaces (t,/2)
        The most likely value  of the environmental weathering half life is assumed to be 14
        days (Fries and Paustenbach 1990).  Miller and Hoffman (1983) analyzed 54
        measurements of t,/; from 25 studies, ranging from 2.8 to 34 days.  These data
        include various categories of depositing substances and vegetation growth forms.

        Plant/soil bioconcentration factor (Bv or Br)
        2.3.4.7.8-PeCDF:  Based on a review of bioconcentration factor data for 29  organic
        chemicals in vegetation,  Travis and Arms (1988) developed the following regression
        equation for Br (U.S. EPA  1993,  1994a):

                             logBr =  1.588 -0.578 log K^                     (V-21-4)

        Assuming log Kow ranges from 5.6 to 7.6, Br ranges from 0.0016 to 0.022, with a
        most likely value of 0.0039 (using log 1^=6.92).
                                                               /•••
        Arsenic:  For arsenic.  Baes  et al. (1984) report the most likely values of the
        plant/soil bioconcentration factors for vegetative (Bv) and non vegetative/ reproductive
Volume V
Appendix V-21
-------
        (Br) portions of food crops and feed plants to be 0.04 and 0.006. respective!) .
        Available plant and product elemental concentration data for arsenic (Baes et al.
        1984. Shacklette et al.  1978, Vinogradov 1959) show values of Bv  ranging from
        0.01  to 0.05 and Br ranging from 0.006 to 0.78.

        Volumetric air-to-leaf biotransfer factor (Bvol)
        2.3.4.7.8-PeCDF:  Bvol is correlated with K^ and the Henry's Law constant (U.S.
        EPA 1993, 1994a):

                       logBvo/ = l.OeSlog/^-log A   -1.654               (V-21-5.
        This correlation is based on data for 14 chemicals collected by Bacci et al.  (1990.
        1992).  Assuming log Kw ranges from 5.6 to 7.6 and H from 1.2xlO"6 to
        1.2xlO~5 atm-m3/mol, Bvol could range from 8.66xl07 to 1.17xlOn.  with a most
        likely value of 1.95X109 (using log Kw=6.92 and H=6.2xlO~6 atm-m3/mol).

        Arsenic: Value not required for modeling.

F.  Dose Parameters
        Intake of Beef
        The intake of beef by subsistence farmers is estimated from a 1987-88 USDA
        national food consumption survey to range from 27 to 251 g/day (USDA 1993,
        1982).  These values correspond to the 5th and 95th percentile consumption rates.
        respectively, as calculated by the methodology described in Chapter VTI.
        Intake of Milk
        The intake of milk by subsistence farmers is estimated from a 1987-88 USDA
        national food consumption survey to range from 20 to 712 g/day (USDA 1993,
        1982).  These values correspond to the 5th and 95th percentile consumption rates.
        respectively, as calculated by the methodology described in Chapter VTJ.
    •   Intake of Pork
        The intake of pork by subsistence farmers is estimated from a- 1987-88 USDA
        national food consumption survey to range from 5 to 127 g/day (USDA 1993,
Volume V
Appendix V-21
-------
         1982).  These values correspond to the 5th and 95th percemile consumption rates.
         respectively, as calculated by the methodology described in Chapter vn.

         Intake of Chicken dRchi<.kel,)
         The intake of chicken by subsistence farmers is estimated from a 1987-88 USDA
         national food consumption survey to range from 18 to 125 g/day (USDA 1^3.
         1982).  These values correspond to the 5th and 95th percentile consumption rates.
         respectively, as calculated by the methodology described in Chapter Vn.
        Intake of Eggs
        The intake of eggs by subsistence farmers is estimated from a 1987-88 USDA
        national food consumption survey to range from 8 to 61 g/day (USDA 1993. 1982)
        These values correspond to the 5th and 95th percentile consumption rates.
        respectively, as calculated by the methodology described in Chapter VH.
     •  Intake of Vegetables (IRAGexpo, IRAGpro,, IR^,
        The intake of vegetables by subsistence farmers is estimated from a 1987-88 USDA
        national food consumption survey to range from 63 to 708 g/day (USDA 1993.
        1982). This includes the consumption of above ground exposed (21 to 234 g/day).
        above ground protected (10 to 113 g/day),  leafy (8 to 92 g/day), and root  (24 to 26Q
        g/day) vegetables.  These values correspond to the 5th and 95th percentile
        consumption rates, respectively, as calculated by the methodology described in
        Chapter VH.

     •  Intake of Fruits (IRFexpo, IRFpro()
        The intake of fruit by subsistence  farmers is estimated from a 1987-88 USDA
        national  food consumption survey  to range  from 42 to 471 g/day (USDA 1993,
        1982).  This includes the consumption of exposed (18 to  198 g/day) and protected
        (24 to 273 g/day) fruit.  These values correspond to the  5th and 95th percentile
        consumption rates, respectively, as calculated by the methodology described in
        Chapter  VII.

    •   Ingestion  of Soil (IR.oU)
        Based on the results of soil exposure models and extrapolations  from soil ingestion
                                                                &*
        data for children,  soil ingestion rates for adults are estimated to range from 0.025
        g/day under most conditions to 0. 100 g/day for people who are  in direct contact
        with contaminated soil (LaGoy 1987).

Volume V
Annendix V-'M                             i c
-------
    •   Body Weight (BW)
        Data and cumulative probability distributions for body weight for over 20.000 adults
        and children (ages 6 months to 74 years) were collected during the second National
        Health and Nutrition Examination Survey (NHANES n), conducted between JQ7b
        and 1980.  For adult male and female (combined) body weights (ages 18 to 75). the
        values corresponding to the 5th and 95th percentiles are 52 and 97 kg. respecmeh
        (AfflC 1994, U.S.  EPA 1990b).


G.  References

American Industrial Health Council (AIHC),  1994.  Exposure factors sourcebook.
    Washington, DC. May.

Arstilla, A. U., G. Reggiani, T. E. Sovari, S. Raisanen, and W. K.  Wipf.  1981.
    Estimation of 2,3,7,8-tetrachlorodibenzo-p-dioxin in goat milk.  Toxicol. Lett. 9:215-
    219.
     i
Bacci. E., D. Calamari, C.  Gaggi, and M. Vighi.  1990. Bioconcentration of organic
    chemical vapors in plant leaves: Experimental measurements and correlation.  Environ.
    Sci. Technol.  24:885-889.

Bacci, E., M.  J. Cerejeira, C. Gaggi, G. Chemello, D. Calamari, and M. Vighi.  1992.
    Chlorinated dioxins:  Volatilization from soils and bioconcentration in plant leaves.
    Bulletin of Environmental Contamination and Toxicology 48(3):401-408.

Baes.  C. F., m, R. D.  Sharp, A. L. Sjoreen, and R. W. Shor.  1984. A review and
    analysis of parameters for assessing transpon of en\ironmentallv released  radlonuclides
    through agriculture.  ORNL-5786.  Oak Ridge. TN: Oak Ridge National Laboratory.
    September.

Bath, D. L.. F. N. Dickinson, H. A. Tucker, and R. D. Appleman.   1985.  Dairy cattle:
    Principles, practices,  problems, profits.  Third edition.  Philadelphia, PA:  Lea &
    Febiger.

Belcher. G. D. and C. C. Travis.  1989.  Modeling support for the rural and municipal
    waste combustion projects:  Final repon on sensitivity and uncertainty analysis for the
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